固相萃取-高效液相色谱法测定水样中硝基苯类化合物

建立了固相萃取-高效液相色谱法测定水样中5种硝基苯类化合物,硝基苯、2,4,6-三硝基甲苯、2,4-二硝基氯苯、邻一硝基氯苯和对-硝基氯苯的方法.对固相萃取,水样预处理和色谱分离条件做了试验并予以优化.采用Porapak RDX固相萃取柱将样品浓缩富集后,以C<,18>色谱柱(250 mm×4.6 mm,5μm)为分离柱,以甲醇和水以体积比55比45的混合液为流动相,在检测波长为260 nm处进行测定.方法检出限(2S/N)为0.8～1.8μg·L-1,相对标准偏差(n=7)在1.1 9/6～5.6%之间,加标回收率在81.5%～101.0%之间.该方法已用于地表水及生活饮用水中的硝基苯类化合物测定.     

液液萃取–气相色谱–质谱法测定水中19种苯胺类化合物

建立了液液萃取–气相色谱–质谱法测定水中19种苯胺类化合物的方法。对液液萃取方法、样品pH、浓缩条件、色谱条件进行了优化,探讨了光氧化降解对苯胺类化合物回收率的影响,在避光条件下,以二氯甲烷为萃取剂,所得提取液在水温为30 ℃、氮气流量为4.0 mL/min的条件下浓缩后供气相色谱–质谱分析测定。19种苯胺类化合物的质量浓度在0.2～5.0 mg/L范围内与色谱峰面积线性关系良好,相关系数R~2大于0.995,检出限为0.013～0.051 μg/L。实际样品平均加标回收率为80.44%～98.79%,相对标准偏差为4.20%～9.41%(n=6)。该方法前处理简便,结果准确,满足水中多种苯胺类化合物的同时测定。     

活性炭纤维固相微萃取-气相色谱法测定海水中的硝基苯类和环酮类化合物

建立了自制活性炭纤维固相微萃取与气相色谱联用测定海水中6种硝基苯类和环酮类化合物的分析方法。优化的萃取条件为: 样品中加NaCl至饱和,在1500 r/min速率搅拌下,于60 ℃水浴中顶空萃取30 min,于280 ℃下解吸2 min。方法的线性范围为0.01～400 μg/L,检出限为1.4～3.2 ng/L,相对标准偏差(RSD,n6)为1.4%～7.8%。海水样品中硝基苯类和环酮类化合物的加标回收率和RSD分别为86.3%～101.8%和3.7%～7.8%。应用所建立的方法对东海近岸表层水样进行测定,其中硝基苯、1,3-二硝基苯、2,6-二硝基甲苯的质量浓度分别为0.756,0.944,0.890 μg/L。实验结果表明,该方法简便、高效、无需有机溶剂,适合于海洋水体中硝基苯类和环酮类化合物的分析。     

分散液液微萃取–气相色谱–质谱法测定水中3种硝基甲苯同分异构体

建立分散液液微萃取-气相色谱–质谱测定水中3种硝基甲苯同分异构体的方法。水中硝基甲苯用分散液液微萃取富集后经CD–5MS色谱柱分离,采用气相色谱质谱法测定。3种硝基甲苯同分异构体的质量浓度在0.0~40.0μg/L范围内与色谱峰面积均具有良好的线性关系,相关系数大于0.999,方法检出限为0.03~0.04μg/L。测定结果的相对标准偏差均小于2%(n=7),样品加标回收率为90.2%~95.9%。该方法操作简便,萃取效率高,有机试剂用量少,适用于环境水样中硝基甲苯的检测。     

液相微萃取-气相色谱/质谱测定水中硝基苯类化合物

建立了水中硝基苯类化合物(硝基苯、1-硝基甲苯、2-硝基甲苯、3-硝基甲苯和邻氯硝基苯)的液相微萃取-气相色谱/质谱检测方法。实验结果显示:甲苯为最佳的萃取剂。确定最佳实验条件为:甲苯体积2μL,萃取时间15 min,搅拌速度300 r/min,萃取温度45℃,溶液pH=5。在此条件下,各目标物的萃取富集倍数为30~38,线性范围为2~250μg/L,检出限为1~2μg/L,测定的相对标准偏差为5%~7%。     

分散液相微萃取-气相色谱/质谱快速分析水中的硝基苯类化合物

建立了分散液相微萃取.气相色谱,质谱快速分析水中硝基苯、对硝基苯、1,3一二硝基苯和2,4-二硝基氯苯的新方法.将含有18μL氯苯(萃取荆)的0.25 mL丙酮(分散剂)作为萃取体系,快速注入到5.0 mL水溶液中.在4000r/min下离心2.0 min后,得到(10.0±0.5)μL沉积相(氯苯),取底部沉积相1.0μL进行气相色谱,质谱分析.方法线性范围0.5～50μg/L(r2=0.9986～0.9994),检出限0.2～0.5μg/L,相对标准偏差4.2%～7.3%(n=5).将该方法用于环境水样的测定,加标回收率72.9%～89.6%.     

微滴液相微萃取技术用于气相色谱-质谱法分析药品中的酞酸酯和对羟基苯甲酸酯

用微滴液相微萃取(SDME)与气相色谱-离子阱质谱联用测定药品中的酞酸酯和对羟基苯甲酸酯。考察了萃取溶剂的种类及用量、微液滴在样品溶液中的深度、萃取时间及搅拌子的搅拌速度对微滴液相微萃取效果的影响。优化的萃取条件:萃取溶剂为1.5 μL甲苯,微液滴在样品溶液中的深度为0.8 cm,搅拌子的搅拌速度为1000 r/min,萃取时间为20 min。该方法的线性范围为0.032~80 mg/L,检出限为0.6 μg/L~1.28 mg/L,加标回收率为95.85%~148.85%,相对标准偏差为3.9%~14.9%。     

环境水样中百菌清残留的单滴微萃取-反相液相色谱测定

应用单滴微萃取(SDME)-反相液相色谱(RPLC)检测了环境水样中的百菌清残留.优化了单滴微萃取条件:环己烷萃取剂6 μL、单滴体积2 μL、搅拌速率350 r/min、萃取时间40 min、水溶液温度35 ℃、无盐度.水样经单滴微萃取后,使用Hypersil C18柱反相液相色谱分离测定百菌清.反相液相色谱条件:100%甲醇流动相、流速1.0 mL/min、柱温25 ℃、224 nm检测.方法的线性范围、检出限、相对标准偏差和富集倍数分别为1.0 ～50 μg/L、0.02 μg/L、6.1%和427倍.采用该法对环境水样中的百菌清残留进行了测定,环境水样的加标回收率为98% ～106%.     

大体积全自动固相萃取气相色谱–质谱法测定水中苯并芘

建立了全自动固相萃取–气相色谱–质谱联用测定水中苯并芘的方法。优化了全自动固相萃取条件,选择C8固相萃取柱萃取水样品中的苯并芘,样品中加入甲醇以增强苯并芘在萃取柱上的保留能力,采用正压大体积六通道同时进样,进样体积为1 000 m L,进样流量20 m L/min,使用二氯甲烷为洗脱溶剂,浓缩至0.5 m L。水中苯并芘的质量浓度在10~200μg/L范围内与其质谱响应值线性关系良好,相关系数为0.995,检出限为2 ng/L。在20~200μg/L加标水平上,苯并芘回收率为85.0%~94.5%,测定结果的相对标准偏差均小于6%(n=6)。该方法操作简单、测定结果准确,可用于水中苯并芘的测定。     

液液萃取–气相色谱法测定地表水中硝基氯苯

建立气相色谱法同时测定地表水中3种硝基氯苯同分异构体的方法。用液液萃取法萃取地表水样品中的硝基氯苯,并对影响萃取效率的因素进行了优化。采用甲苯作为萃取溶剂,以DB–1701毛细管色谱柱(30 m×0.32mm,0.25μm)进行分离,气相色谱法检测地表水中硝基氯苯的含量。硝基氯苯的质量浓度在0.00~40.0μg/L范围内与其色谱峰面积呈良好的线性关系,线性相关系数均大于0.995,检出限为0.07~0.08μg/L,低于《地表水环境质量标准》限值。加标回收率为85.3%~98.0%,测定结果的相对标准偏差均小于2%(n=6)。该方法操作简单,重现性好,准确度好,检测速度快,适用于地表水中硝基氯苯的测定。     

Comparative study of pesticide multi-residue extraction in tobacco for gas chromatography-triple quadrupole mass spectrometry

Coacervates made of surfactant aggregates, namely aqueous and reverse micelles and vesicles, were firstly used as solvents in single-drop microextraction (SDME) and proposed for the extraction and concentration of chlorophenols prior to liquid chromatography. The formation of coacervate drops in the needle tip of conventional microsyringes depended on the type of intermolecular forces established between the surfactant headgroups making up the supramolecular aggregates; hydrogen bond interactions were strong enough to permit the formation of spherical drops. Stability of 1-50 microL coacervate drops was achieved by introducing the microsyringe needle tip in a PTFE rod, the end of which had been machined out with a heated flanging-tool to get circular flanges (diameters in the range 3.5-6 mm). The parameters affecting the efficiency of single-drop coacervative microextraction (SDCME) were investigated using vesicular coacervates as a solvent and 2-chlorophenol (CP), 2,4-dichlorophenol (DCP), 2,4,6-trichlorophenol (TCP) and pentachlorophenol (PCP) as model analytes. Coacervative microextraction dynamics fit to the general rate equation of liquid-liquid extraction. The effect of variables such as extraction time, drop volume, stirring rate, pH and temperature, on the extraction of chlorophenols was similar to that described for organic solvent drops. Electrolyte concentrations above 0.1 M caused drop instability. Under the optimum conditions, detection limits were in the range 0.1-0.3 microg L(-1). The relative standard deviation was between 4.3 and 5.6 at 20 microg L(-1) spiked level. The method was applied to the determination of the four chlorophenols in wastewater, superficial water from a reservoir and groundwater and the recoveries were in the range 79 and 106% at 5-20 microg L(-1) spiked level.     

Determination of chlorobenzenes in water by drop-based liquid-phase microextraction and gas chromatography-electron capture detection

A drop-based liquid phase microextraction and gas chromatographic-electron capture detection (GC-ECD) method was described for the determination of chlorobenzenes including chlorobenzene, 1,2-dichlorobenzene, 1,3-dichlorobenzene, 1,4-dichlorobenzene and 1,2,3-trichlorobenzene in 5 ml of water. The method used 2 microl of n-hexane as extraction solvent, 5 min extraction time, a stirring rate of 600 rpm and sample ionic strength of 3 M maintained with sodium chloride at 25 degrees C (ambient temperature). The limits of detection (LODs) ranged from 0.004 microg l(-1) (for 1,3-dichlorobenzene) to 0.008 microg l(-1) (for monochlorobenzene). The dynamic linear range for all investigated chlorobenzenes was 1-50 microg l(-1). Recoveries of chlorobenzenes from fortified distilled water are over 90% for three different fortification levels (5, 15 and 45 microg l(-1)) and relative standard deviations of the recoveries are below 6%. Analysis of fortified (5 microg l(-1)) real water samples revealed that matrices had no adverse effect on extraction efficiency of proposed method. The recovery of fortified real water samples was from 90 to 94% with relative standard deviations below 6%.     

Dispersive liquid-liquid microextraction followed by reversed phase HPLC for the determination of decabrominated diphenyl ether in natural water

A simple, rapid, and efficient method, dispersive liquid-liquid microextraction (DLLME), has been developed for the extraction and preconcentration of decabrominated diphenyl ether (BDE-209) in environmental water samples. The factors relevant to the microextraction efficiency, such as the kind and volume of extraction and dispersive solvent, the extraction time, and the salt effect, were optimized. Under the optimum conditions (extraction solvent: tetrachloroethane, volume, 22.0 microL; dispersive solvent: THF, volume, 1.00 mL; extraction time: below 5 s and without salt addition), the most time-consuming step is the centrifugation of the sample solution in the extraction procedure, which is about 2 min. In this method, the enrichment factor could be as high as 153 in 5.00 mL water sample, and the linear range, correlation coefficient (r(2)), detection limit (S/N = 3), and precision (RSD, n = 6) were 0.001-0.5 microg/mL, 0.9999, 0.2 ng/mL, and 2.1%, respectively. This method was successfully applied to the extraction of BDE-209 from tap, East Lake, and Yangtse River water samples; the relative recoveries were 95.8, 92.9, and 89.9% and the RSD% (n = 3) were 1.9, 2.7, and 3.5%, respectively. Comparison of this method with other methods, such as solid-phase microextraction (SPME), and single-drop microextraction (SDME), indicates that DLLME is a simple, fast, and low-cost method for the determination of BDE-209, and thus has tremendous potential in polybrominated diphenyl ethers (PBDEs) residual analysis in environmental water samples.     

Analysis of nitrobenzene compounds in water and soil samples by graphene composite-based solid-phase microextraction coupled with gas chromatography–mass spectrometry

In this work, solid-phase microextraction coupled with gas chromatography–mass spectrometry was developed to determine trace levels of nitrobenzene compounds in water and soil samples. Graphene was chosen as the extraction material and its composite was coated on a stainless steel wire through sol–gel technique for the solid phase microextraction. The key parameters influencing the extraction efficiency were optimized. Under the optimal conditions, the linearity for the compounds was observed in the range of 0.02–15.0 mg/L for water samples, and 0.2–60.0 mg/kg for soil samples, with the correlation coefficients（r） of 0.9966–0.9987. The limits of detection of the method were 0.0025–0.005 mg/L for water samples, and 0.02–0.04 mg/kg for soil samples. The recoveries for the spiked samples were in the range of 72.0%–113.2%, and the precision, expressed as the relative standard deviations, was less than 12.1%.     

Validated dispersive liquid-liquid microextraction for analysis of organophosphorous pesticides in water

Dispersive liquid-liquid microextraction (DLLME) combined with gas chromatography and mass spectrometry (GC-MS) was applied to the determination of six organophosphorous pesticides (OPPs) in water samples. The analytes included in this study were prophos, diazinon, chlorpyrifos methyl, methyl parathion, fenchlorphos and chlorpyrifos. Several extraction and dispersion solvents were tested for dispersive liquid-liquid microextraction of these analytes and the best results were obtained using chloroform as extraction solvent and 2-propanol as dispersion solvent. Calibration curves of the analytes in water samples were constructed in the concentration range from 100 to 1100 ng/L for prophos, diazinon and methyl parathion and in the range from 100 to 1000 ng/L for chlorpyrifos methyl, fenchlorphos and chlorpyrifos. Limits of detection (LODs) were in the range of 1.5-9.1 ng/L and limits of quantification (LOQs) were in the range of 5.1-30.3 ng/L, below the maximum admissible level for drinking water. Relative standard deviations (RSDs) were between 6.5 and 10.1% in the concentration range of 100-1000 ng/L. The relative recoveries (%RRs) of tap, well and irrigation water samples fortified at 800 ng/L were in the range of 46.1-129.4%, with a larger matrix effect being detected in tap water.     

Metal–organic framework UiO‐67‐coated fiber for the solid‐phase microextraction of nitrobenzene compounds from water

A sol–gel coating technique was applied for the preparation of a solid‐phase microextraction fiber by coating the metal–organic framework UiO‐67 onto a stainless‐steel wire. The prepared fiber was explored for the headspace solid‐phase microextraction of five nitrobenzene compounds from water samples before gas chromatography with mass spectrometric detection. The effects of the extraction temperature, extraction time, sample solution volume, salt addition, and desorption conditions on the extraction efficiency were optimized. Under the optimal conditions, the linearity was observed in the range of 0.015–12.0 μg/L for the compounds in water samples, with the correlation coefficients (r) of 0.9945–0.9987. The limits of detection of the method were 5.0–10.0 ng/L, and the recoveries of the analytes from spiked water samples for the method were in the range of 74.0–102.0%. The precision for the measurements, expressed as the relative standard deviation, was less than 11.9%.     

气相-动态顶空进样技术用于矿泉水中61种有机物的同时检测

采用气相动态顶空进样-气相色谱-质谱法(D-HS-GC-MS)同时分析矿泉水中氯乙烯、氯丁二烯、硝基苯、硝基氯苯、1,3,5-三氯苯和其他54种常见挥发性有机物,方法检出限除硝基苯、2-硝基氯苯、3+4-硝基氯苯分别为5.9、6.4和9.9!g/L外,其余均介于0.18~0.48!g/L.D-HS-GC-MS法均有良好的精密度和精确度,1.00和2.00!g/L空白加标样品的测定结果精密度分别介于5.8%~19%和2.0%~11%(n=7),市售矿泉水样品的加标回收率介于92.4%~108%.     

Multiple headspace single-drop microextraction-a new technique for quantitative determination of styrene in polystyrene

Single-drop microextraction (SDME), an emerging miniaturised extraction technique, was for the first time combined with multiple headspace extraction (MHE) to enable the quantitative determination of volatiles in solid matrixes by SDME technique. The concept of multiple headspace single-drop microextraction (MHS-SDME) was then applied for quantitative determination of styrene in polystyrene (PS) samples. Good linearity for the multiple headspace extraction was obtained when the migration of styrene was facilitated by grinding the samples and incubating them for 1 h at 150 degrees C prior the first extraction. Two microlitres of butyl acetate was used as the single-drop microextraction solvent and the extraction time was 5 min per cycle. The relative standard deviation (RSD) for single-drop microextraction of styrene standard at n=6 was 7.6%. Linearity was shown for styrene concentrations between 0.005 and 0.75 microg/ml (R2=0.999). This corresponds to total amount of styrene between 0.1 and 15 microg. The limit of quantitation for styrene standard at S/N 10 was 0.005 microg/ml. The developed method was validated against and showed good agreement with an earlier reported dissolution-precipitation method.     

Determination of triazine herbicides in aqueous samples by dispersive liquid-liquid microextraction with gas chromatography-ion trap mass spectrometry

A simple and rapid new dispersive liquid-liquid microextraction technique (DLLME) coupled with gas chromatography-ion trap mass spectrometric detection (GC-MS) was developed for the extraction and analysis of triazine herbicides from water samples. In this method, a mixture of 12.0 microL chlorobenzene (extraction solvent) and 1.00 mL acetone (disperser solvent) is rapidly injected by syringe into the 5.00 mL water sample containing 4% (w/v) sodium chloride. In this process, triazines in the water sample are extracted into the fine droplets of chlorobenzene. After centrifuging for 5 min at 6000 rpm, the fine droplets of chlorobenzene are sedimented in the bottom of the conical test tube (8.0+/-0.3 microL). The settled phase (2.0 microL) is collected and injected into the GC-MS for separation and determination of triazines. Some important parameters, viz, type of extraction solvent, identity and volume of disperser solvent, extraction time, and salt effect, which affect on DLLME were studied. Under optimum conditions the enrichment factors and extraction recoveries were high and ranged between 151-722 and 24.2-115.6%, respectively. The linear range was wide (0.2-200 microg L(-1)) and the limits of detection were between 0.021 and 0.12 microg L(-1) for most of the analytes. The relative standard deviations (RSDs) for 5.00 microg L(-1) of triazines in water were in the range of 1.36-8.67%. The performance of the method was checked by analysis of river and tap water samples, and the relative recoveries of triazines from river and tap water at a spiking level of 5.0 microg L(-1) were 85.2-114.5% and 87.8-119.4%, respectively. This method was also compared with solid-phase microextraction (SPME) and hollow fiber protected liquid-phase microextraction (HFP-LPME) methods. DLLME is a very simple and rapid method, requiring less than 3 min. It also has high enrichment factors and recoveries for the extraction of triazines from water.     

Determination of some organophosphorus and azole group pesticides in water samples by dispersive liquid-liquid microextraction coupled with GC/MS

A dispersive liquid-liquid microextraction (DLLME) procedure coupled with GC/MS detection is described for preconcentration and determination of some organophosphorus and azole group pesticides from water samples. Experimental conditions affecting the DLLME procedure were optimized by means of an experimental design. A mixture of 60 microL chlorobenzene (extraction solvent) and 750 microL acetonitrile (disperser solvent), 3.5 min extraction time, and 7.5 mL aqueous sample volume were chosen for the best recovery by DLLME. The linear range was 1.6-32 microg/L. The LOD ranged from 48.8 to 68.7 ng/L. The RSD values for organophosphorus and azole group pesticides at spiking levels of 3, 6, and 9 microg/L in water samples were in the range of 1.1-12.8%. The applicability and accuracy of the developed method were determined by analysis of spiked water samples, and the recoveries of the analyzed pesticides from artesian, stream, and tap waters at spiking levels of 3, 6, and 9 microg/L were 89.3-105.6, 89.5-103.0, and 92.0-111.3%, respectively.