固相萃取富集-高效液相色谱法分离检测水中3种苯脲除草剂

建立了固相萃取富集-高效液相色谱分析水中3种痕量苯脲除草剂——利谷隆、敌草隆、灭草隆的方法。C18固相萃取柱富集水中待测组分,高效液相色谱以Hypersil ODS柱为分析柱,优化出的色谱条件为：流动相为甲醇／水=60：40(V／V);流速为0．7mL／min;柱温为30℃。本法操作简便、灵敏、回收率高。     

整体柱在线固相微萃取-高效液相色谱同步富集检测水中的苯氧羧酸类除草剂

采用C18毛细管整体柱作为固相微萃取整体柱,构建在线固相微萃取-高效液相色谱联用系统,同步富集检测环境水样中的5种苯氧羧酸类除草剂。详细考察了联用系统运行条件对富集检测的影响。联用系统运行最佳参数为:固相微萃取整体柱长度20 cm,进样流速0.04 mL/min,进样13 min,洗脱流速0.02 mL/min,洗脱5 min。在最佳条件下,5种苯氧羧酸类除草剂的检出限为:9 μg/L (苯氧丙酸)、4 μg/L (2-(2-氯)-苯氧丙酸)、4 μg/L (2-(3-氯)-苯氧丙酸)、5 μg/L (2,4-二氯苯氧乙酸)、5 μg/L (2-(2,4-二氯苯氧基)丙酸)。与HPLC系统直接进样对比,联用系统对5种检测对象表现出优良的富集能力。5种苯氧羧酸类除草剂的回收率在79.0%~98.0%之间(RSD≤3.9%)。该方法成功应用于水样中5种苯氧羧酸类除草剂的检测,结果令人满意。     

固相膜萃取-超声洗脱-原位衍生法分析水中不同极性农药残留

建立了水中极性除草剂和非极性杀虫剂固相膜萃取-超声洗脱-原位衍生-气相色谱质谱方法。在样pH≈3时,采用C8固相萃取膜,10 min可完成1000 mL水中两类化合物的萃取;将膜片置于反应瓶中,加入2 mL丙酮溶剂和衍生试剂,对杀虫剂进行超声洗脱、对除草剂进行洗脱衍生。其洗脱、衍生时间为30 min。以HP-5MS(30 m×0.25 mm×0.25μm)为分析柱,采用负化学源技术在10 min内完成两类物质的检测。由于衍生试剂与酸性除草剂是特定的官能团之间的反应,并且衍生时间较短,因此杀虫剂的回收率不受影响。方法实现了不同极性有机物的同时萃取、同时检测。在10~250μg/L线性范围内各组分线性关系良好,相关系数R2>0.9978,检出限<1.0μg/L。不同基质、不同浓度的加标回收率在88%~107%之间;相对标准偏差在3.6%~9.7%之间。     

固相萃取-高效液相色谱法同时检测大米中12种磺酰脲类除草剂的残留

建立了固相萃取前处理净化技术-高效液相色谱（HPLC）同时检测大米中12种磺酰脲类除草剂残留的方法。采用ENVITM-18(C18)硅胶柱和ENVI-Carb(GCB)石墨化碳柱对样品进行净化、萃取,采用C8柱,以乙腈和5 mmol/L 冰乙酸混合溶剂为流动相进行梯度洗脱,在240 nm下进行检测。12种磺酰脲类除草剂在0.01~0.50 μg/g添加范围内的回收率为72.2%~106.5%,相对标准偏差为0.6%~6.4%,检出限为0.01~0.02 μg/g。     

固相萃取富集-高效液相色谱法测定环境水中多菌灵和噻菌灵

建立了以固相萃取技术富集，高效液相色谱法进行分离和检测多菌灵和噻菌灵2种杀菌剂的方法。环境水中的多菌灵和噻菌灵用3M Empore 6mL C18 Cartridge进行固相萃取。以Hypersil ODS柱为分析柱，优化得到高效液相色谱分离条件：流动相为甲醇-水(50：50，V/V)；流速为0．7mL／min；柱温为55℃；在286nm波长下检测，检出限为0．05mg／L。本法操作简便，灵敏，回收率高。     

水中苯氧羧酸类除草剂的液相色谱-串联质谱测定方法研究

建立了固相萃取(SPE)/超高效液相色谱-三重四极杆串联质谱(UPLC-MS/MS)同时测定水中8种苯氧羧酸类除草剂残留的方法。过滤后的样品经HLB固相萃取柱富集净化后,采用BEH C18柱,以2 mmol/L乙酸铵-乙腈作为流动相进行梯度洗脱,采用串联质谱进行检测。8种苯氧羧酸类除草剂在0.8～100μg/L质量浓度范围内线性关系良好(r=0.995 8～0.999 6),回收率为74%～90%,相对标准偏差为1.0%～12.0%,方法检出限(3S)为1.0～1.8 ng/L。该方法快速、灵敏,适用于水体中8种苯氧羧酸类除草剂残留的测定。     

固相萃取-高效液相色谱法测定水中的多环芳烃

建立了固相萃取-一高效液相色谱法测定水中多环芳烃的方法。水样经L-18固相萃取柱吸附后用二氯甲烷洗脱,氮吹干后换甲醇溶剂。反相C18柱为色谱柱;水、甲醇为流动相进行梯度洗脱,流速为1．0mL／min;柱温为30℃;检测器为荧光检测器、紫外检测器。方法的检出限为0．00006-0.03μg／L,回收率为80％～110％,测定结果的相对标准偏差为0．1％～3．6％（n=5）。方法适合于水中16种多环芳烃的测定。     

环境水中甲基对硫磷、对硫磷和辛硫磷农药残留的SPE-HPLC分析

采用离线固相萃取 (SPE)富集 -高效液相色谱(HPLC)分离和紫外分光光度法检测 ,对环境水中甲基对硫磷、对硫磷和辛硫磷3种有机磷农药进行分析;固相萃取用C18 萃取柱 ,用甲醇洗脱 ,高效液相色谱分离以Shim_PackCLCODS柱(150mm×4.6mmid,5μm)为分离柱 ,流动相为甲醇 -水(体积比70∶30) ,紫外检测波长为280nm;该法稳定可靠 ,回收率高     

固相萃取富集高效液相色谱法测定苯氧乙酸和2,4-二氯苯氧乙酸

建立了以固相萃取技术进行富集 ,高效液相色谱法进行分离和检测苯氧乙酸和 2 ,4 二氯苯氧乙酸的方法。环境水中的苯氧乙酸和 2 ,4 二氯苯氧乙酸用Sep PakC18Cartridge进行固相萃取。液相色谱的条件是 :Shim PackCLCODS柱为分析柱 ;甲醇 水 (9∶1,V/V)为流动相 ;流速为 1mL/min ;在UV 2 75nm波长下进行检测。本法具有良好的灵敏度和重现性     

固相萃取和高效液相色谱相结合快速测定苦瓜甙A的含量(英文)

 建立了一个快速、简单、准确的固相萃取和高效液相色谱相结合的测定苦瓜甙A含量的方法。样品经石墨碳固相萃取管 (3mL/ 2 5 0mg)纯化后以高效液相色谱检测。色谱柱为C18,流动相为V(乙腈 )∶V(甲醇 )∶V(5 0mmol/L磷酸二氢钾缓冲液 ) =2 5∶2 0∶6 0 ,流速为 0 .8mL/min ,检测波长为 2 0 8nm。标准曲线自 10mg/L到 10 0 0mg/L呈线形关系 (r2 =0 .9992 )。该方法具有很好的重现性 ,日内或日间的相对标准偏差和相对平均误差均小于 10 %。样品回收率大于 90 %。     

玉米中9种磺酰脲类除草剂的超高效液相色谱-串联质谱法同时测定

采用超高效液相色谱-串联四极杆质谱(UPLC-MS/MS),在多反应监测(MRM )模式下建立了玉米中9种磺酰脲类除草剂残留的定性定量分析方法.样品浸泡后采用甲醇-丙酮(体积比1:1)提取、浓缩,经C18固相萃取柱净化处理.采用UPLC-ESI MS/MS方法测定,外标法定量.9种磺酰脲类除草剂在0.05～2.0 mg...     

Rapid analysis of triazolopyrimidine sulfoanilide herbicides in waters and soils by high-performance liquid chromatography with UV detection using a C18 monolithic column

In this work, the simultaneous analysis of five triazolopyrimidine sulfoanilide herbicides (flumetsulam, florasulam, metosulam, cloransulam-methyl, and diclosulam) by HPLC using UV detection and a C18 monolithic column is proposed. The mobile phase which was composed of ACN, water, and formic acid was pumped at a high flow rate (5 mmL/min) providing an analysis time of all the compounds in less than 2.3 min. The LODs were in the low microg/L range (i.e. between 60 microg/L for flumetsulam and 90 microg/L for florasulam) and the calibration curves showed good linearity (R2 > 0.9949). The method was applied to the analysis of these compounds in spiked mineral and tap waters and soils after an SPE preconcentration procedure using C18 cartridges. Mean recovery values ranged between 35 and 110% for water samples providing LODs of the whole procedure in the low ng/L level, down to 280 ng/L, and between 77 and 92% for soil samples with LODs down to 9.38 microg/kg. This is the first time that this family of pesticides is simultaneously analyzed in both types of samples by HPLC and also using a monolithic column.     

Comparison of Different Sorbents for Solid-Phase Extraction of Phenoxyalkanoic Acid Herbicides

An HPLC procedure for determination of phenoxyalkanoic acid herbicides in water samples is proposed. The analytical column Phenomenex C18(2) Luna 5 µm and UV detection at 225 nm were applied. Baseline resolution was achieved in isocratic mode with a mobile phase consisting of acetonitrile/acetic acid (40/60, v/v), adjusted to pH 2.5. SPE sorbents – C₁₈ BondElut, phenyl-silica, LiChrolut SAX and polymeric sorbents – were compared for isolation and preconcentration of 6 phenoxyalkanoic acid herbicides. Higher (above 95%) and more reproducible recoveries were obtained with polymeric and phenyl-silica sorbents using pure methanol for elution. The method was tested for river water samples with the limit of detection in the range of 2–3 µg L⁻¹ (for 50 mL sample) and a reproducibility of 5% RSD.     

Screening method for phenoxy acid herbicides in ground water by high-performance liquid chromatography of 9-anthryldiazomethane derivatives and fluorescence detection

A high-performance liquid chromatographic (HPLC) method for phenoxy acid herbicides using precolumn derivatization with 9-anthryldiazomethane (ADAM) is presented. The phenoxy acid herbicides investigated were (2,4-dichlorophenoxy)acetic acid, (4-chloro-2-methylphenoxy)acetic acid, 2-(4-chloro-2-methylphenoxy)propionic acid and (4-chloro-2-methylphenoxy)butyric acid. These herbicides reacted with ADAM under mild conditions and were converted into the corresponding fluorescent derivatives. The ADAM derivatives were separated by reversed-phase HPLC and determined using a fluorescence detector. The detection limits were about 500 pg per injection. For the application of ADAM to the determination of these herbicides in ground waters, the recoveries were more than 93% and the average relative standard deviation was 6.0% at 0.5 microgram/l. The procedure is useful as a screening method for phenoxy acid herbicides in ground water samples.     

Pre‐concentration of trace amount of bisphenol A in water samples by palm leaf ash and determination with high‐performance liquid chromatography

Palm leaf ash was characterized and used as low‐cost adsorbent for solid‐phase extraction and preconcentration of bisphenol A (BPA) in real water samples. Analysis of BPA was carried out using HPLC involving Eurospher 100–5‐C₁₈ (25 cm × 4.5 mm, particle size 5 μm) column and water–acetonitrile (40:60, v/v) as mobile phase. The adsorption was achieved quantitatively at a pH of 6 with elution by 3 mL acetonitrile. The limits of detection and enrichment factor were 0.02 μg L^?1 and 333, respectively. Under optimum conditions the relative standard deviation (RSD) was 2% (n = 10). Comparison of qualification criteria of presented preconcentration procedure with other research indicated that palm leaf ash adsorbent was better than many of the adsorbents in terms of cost and reusability. Also, the limit of detection, precision and enrichment factor were comparable and even better than the previously reported methods. Finally, the efficiency of method was computed by determination of trace amounts of BPA in sea, river, mineral and tap waters with recoveries of 93.3–105.5% and RSDs of 0.61–3.12%.. Briefly, the developed solid‐phase extraction and Preparative layer chromatography (PLC) methods may be used for bisphenol A monitoring in any environmental water sample. Copyright © 2016 John Wiley & Sons, Ltd.     

Determination of Phenylureas Herbicides in Foodstuffs Based on Matrix Solid-Phase Dispersion Extraction and RP-LC with UV Detection

A new method for simultaneous determination of seven kinds of phenylurea herbicides (PUHs) in solid foodstuffs was established based on matrix solid phase dispersion (MSPD)–RP-LC. The procedure of MSPD is simple and not time-consuming. C₁₈-bonded silica and anhydrous alumina were, respectively, used as dispersion sorbent and purificant, and dichloromethane as extraction reagent. Under the optimum conditions, seven kinds of herbicides were separated completely within 30 min, response was a linear function of concentration over the range 2.5–500 μg L^?1 with good correlation coefficients (>0.99) and lower detection limits (0.25 and 0.5 μg L^?1). Intra-day and inter-day precision of the peak areas for seven PUHs were less than 3.7 and 5.3%. The new method was used to detect seven PUHs in four kinds of solid foodstuffs with average recoveries range from 73.1 to 101%.     

柱后紫外光解荧光衍生液相色谱法测定蔬菜中残留的15种苯脲除草剂

建立了蔬菜中15种苯脲除草剂残留的固相萃取-在线柱后紫外光分解和衍生化的高效液相色谱荧光检测分析方法。样品用乙腈提取,弗罗里硅土固相萃取柱净化,目标化合物由反相C18柱分离,经柱后紫外光分解和衍生化后进行荧光检测。对样品的前处理条件、液相色谱分离、柱后紫外光分解和衍生条件等进行了详细的研究。15种苯脲除草剂的高效液相色谱分离在乙腈-水梯度洗脱下完成,目标物的保留时间为9～31 min,线性范围内线性关系良好,相关系数为0.9986~1.0000;在洋葱、菠菜、黄瓜等样品中3个加标水平的平均回收率(n=3)为75.3%～121.6%,相对标准偏差为0.4%-11.6%;15种苯脲除草剂在蔬菜中的检出限为0.005～0.05 mg/kg。该方法操作简便、灵敏度高、选择性好,符合多种农药残留分析的要求。     

Determination of phenoxyacid herbicides and their phenolic metabolites in surface and drinking water.

An evaluation was made of the feasibility of using reversed-phase liquid chromatography/tandem mass spectrometry with an electrospray interface (LC/ESI-MS/MS) to measure traces of phenoxyacid herbicides and their metabolites in surface and drinking water samples. The procedure involved passing 0.5 L of river and drinking water samples through a 0.5 g graphitized carbon black (GCB) extraction cartridge. Recovery was higher than 85% irrespective of the aqueous matrix in which the analytes were dissolved. A conventional 4.6-mm i.d. reversed-phase LC C-18 column operating with a mobile phase flow rate of 1 mL/min was used to chromatograph the analytes. A flow of 200 microL/min of the column effluent was diverted to the ESI source. The limits of detection (signal-to-noise ratio = 3) of the method for the pesticides considered in drinking and surface water samples are less than 0.1 ng/L for phenoxyacid herbicides, and about 5-10 ng/L for their metabolites (2,4-dichlorophenol and 4-chloro-2-methylphenol).     

Magnetic solid-phase extraction of sulfonylurea herbicides in environmental water samples by Fe3O4@dioctadecyl dimethyl ammonium chloride@silica magnetic particles

A magnetic solid phase extraction (MSPE) method coupled with high-performance liquid chromatography (HPLC) was proposed for the determination of five sulfonylurea herbicides (bensulfuron-methyl, prosulfuron, pyrazosulfuron-ethyl, chlorimuron-ethyl and triflusulfuron-methyl) in environmental water samples. The magnetic adsorbent was prepared by incorporating Fe₃O₄ nanoparticles and surfactant into a silica matrix according to a sol–gel procedure, which can provide surfactant free extracts during the eluting step to avoid chromatographic interference. The prepared adsorbent was used to extract the sulfonylurea herbicides in several kinds of water samples. The main factors affecting the extraction efficiency, including desorption conditions, extraction time, sample volume, and sample solution pH were optimized. Under the optimum conditions, good linearity was obtained within the range of 0.2–50.0 μg L⁻¹ for all analytes, with correlation coefficients ranging from 0.9993 to 0.9999. The enrichment factors were between 1200 and 1410, and the limits of detection were between 0.078 and 0.10 μg L⁻¹. The proposed method was successfully applied in the analysis of sulfonylurea herbicides in environmental samples (tap, reservoir, river, and rice field). The recoveries of the method ranged between 80.4% and 107.1%. This study reported for the first time the use of MSPE procedure in the preconcentration of sulfonylurea herbicides in environmental samples. The procedure proved to be efficient, environmentally friendly, and fast.     

Rapid and sensitive detection of the phenoxy acid herbicides in environmental water samples by magnetic solid‐phase extraction combined with liquid chromatography–tandem mass spectrometry

Phenoxy acid herbicides are widely used herbicides that play an important role in improving the yield and quality of crops. However, some research has shown that this kind of herbicide is poisonous to human and animals. In this study, a rapid and sensitive method was developed for the detection of seven phenoxy acid herbicides in water samples based on magnetic solid‐phase extraction followed by liquid chromatography and tandem mass spectrometry. Magnetic amino‐functionalized multiwalled carbon nanotubes were prepared by mixing bare magnetic Fe₃O₄ nanoparticles with commercial amino‐functionalized multiwalled carbon nanotubes in water. Then the amino‐functionalized multiwalled carbon nanotubes were used to enrich phenoxy acid herbicides from water samples based on hydrophobic and ionic interactions. The effects of experimental variables on the extraction efficiency have been studied in detail. Under the optimized conditions, the method validation was performed. Good linearities for seven phenoxy acid herbicides were obtained with squared regression coefficients ranging from 0.9971 to 0.9989. The limits of detection ranged from 0.01 to 0.02 μg/L. The method recoveries of seven phenoxy acid herbicides spiked at three concentration levels in a blank sample were from 92.3 to 103.2%, with inter‐ and intraday relative standard deviations less than 12.6%.