源内碰撞诱导解离质谱技术在农药残留分析中的应用

选择了两种难挥发、强极性及热不稳定农药（三嗪类除草剂－阿特拉津及有机磷类农药－二嗪农）进行了其碎片谱研究,６种农药（阿特拉津、西草净、西玛津,杀草净、涕戚、绿麦隆）混合物经过ＨＰＬＣ良好分离后实现了ＨＰＬＣ／ＡＰＣＩ／ＣＩＤＭＳ的测定,获得了各自的特征碎片谱,采用ＣＩＤ技术,既可得到待测物的分子量,又可得结构信息。     

磁固相萃取-气相色谱-火焰光度检测联用测定果汁中的有机磷农药

制备了苯乙烯（St）和甲基丙烯酸（MAA）共聚物改性的磁性微球Fe₃O₄@P（St-co-MAA）,并将其作为磁固相萃取吸附剂,建立了磁固相萃取（MSPE）-气相色谱（GC）-火焰光度检测（FPD）联用分析有机磷农药（OPPs）残留的新方法。以5种有机磷农药（二嗪农、甲基毒死蜱、杀螟硫磷、毒死蜱和喹硫磷）为目标分析物,考察并优化了吸附和解吸条件,确定了最佳实验条件。在最优的实验条件下,方法对5种OPPs的检出限（S/N=3）为0.013~0.305 μg/L,方法的相对标准偏差（RSD,n=7）为3.1%~8.8%,富集倍数为406~951,线性范围达3个数量级。将该方法应用于新鲜番茄汁、草莓汁样品中的OPPs残留分析,加标回收率为85.4%~118.9%。该方法具有检出限低、分析速度快、富集倍数高等优点,为有机磷农药的残留分析提供了新的技术平台。     

溶剂浮选光度法测定痕量铜

提出了利用溶剂浮选富集ＤＤＴＣ－Ｃｕ（Ⅱ）体系测定水样中痕量铜的方法（ＤＤＴＣ为二乙胺二硫代甲酸钠）。质量浓度的检出限为０．０５ｎｇ·ｍＬ＾－１,线性范围为０．０￣６．０ｎｇ·ｍＬ＾－１,测定含Ｃｕ（Ⅱ）４．０ｎｇ·ｍＬ＾－１的样品,相对标准偏差为０．８５％,已用于天然水中Ｃｕ（Ⅱ）的测定。     

气相色谱-火焰光度法测定土壤中有机磷农药残留

建立了气相色谱-火焰光度(GC-FPD)分析土壤中敌敌畏、氧化乐果、二嗪农、乐果、甲基对硫磷、马拉硫磷、对硫磷、水胺硫磷、喹硫磷等9种有机磷农药残留量的方法。样品用丙酮-二氯甲烷(1:3)提取,浓缩、定容后用Hp-5MS(30m×0.25 mm×0.25μm)毛细管柱分离,FPD检测器检测。方法回收率在68.71%～110.39%之间;RSD在5.5%～11%之间;检出限在0.397～1.60μg/mL之间,方法可用于环境土壤样品中有机磷农药残留的测定。     

铂—钯共显色衍生络合物的高效液相色谱研究

研究了Ｐｄ（Ⅱ）和４，４＇－二（二乙氨基）苯硫酮（ＢＤＰＴＫ）共显色所生成的Ｐｔ（Ⅱ）络合物，于Ｎｕｃｌｅｏｓｉｌ Ｃ８柱上，用含３×１０＾－３ｍｏｌ／Ｌ ＣＳＡ和０．０２ｍｏｌ／Ｌ ＨＡｃ－ＮａＡｃ（ｐＨ３．５）的乙腈－丙酮－水（７２：５：２３，Ｖ／Ｖ）作流动相（１．０ｍｌ／ｍｉｎ）分离并检测。Ｐｔ的校正曲线的线性范围为０．２～３．０μｇ／ｍｌ，Ｐｔ检测限为０．７ｎｇ。此方法已应用于抗癌药物顺铂     

高分子多孔微球富集—HPLC法测定水体中的有机磷

本文提出应用国产高分子多孔微球－ＧＤＸ系列富集－反相高效液相色谱法测定废水中久效磷、乐果、甲基对硫磷三种有机磷农药分析方法。三种不同型号色谱固定相（ＧＤＸ－１０２，ＧＤＸ－３０１和ＧＤＸ－５０１）对水体中ｎｇ／ｍＬ级久效磷、乐果和甲基以硫磷的富集效率分别达到８５％、８２％和９３％以上，采用μ－Ｂｏｎｄａｐａｋ Ｃ１８作固定相，以６０％甲醇水溶液作流动相，对三种有机磷农药的分离度可达到１．２以上。本     

铟（Ⅲ）－PMBP－Ferron极谱络合吸附波研究

在ＨＣｌ－ＮａＡｃ介质（ｐＨ２．５）中，可获得灵敏的Ｉｎ（Ⅲ）－ＰＭＢＰ－Ｆｅｒｒｏｎ极谱络合吸附波，峰电位在－０．６５Ｖ处（ｖｓ·ＳＣＥ），检出限为０．０４ｎｇ／ｍＬＩｎ。峰电流与铟浓度在０．０８～２００ｎｇ／ｍＬ范围内呈线性关系。本法测定工业废水中的痕量铟，结果满意。本文还研究了极谱波的性质和机理。     

分散液液微萃取-气相色谱法快速测定水中23种有机磷农药

建立了分散液液微萃取(DLLME)的新型样品前处理方法,并采用气相色谱/火焰光度检测器对饮用水中的治螟磷、甲拌磷、二嗪农、乙拌磷、甲基毒死蜱、甲基对硫磷、皮蝇磷、杀螟松、马拉硫磷、毒死蜱、倍硫磷、对硫磷、溴硫磷、嘧啶磷、甲基异硫磷、稻丰散、杀扑磷、丙溴磷、乙硫磷、三唑磷、三硫磷、哒嗪硫磷、亚胺硫磷23种痕量有机磷农药残...     

钴(Ⅱ)-β-巯基丙酸-NaNO_2体系的极谱催化波研究

在ｐＨ３．８的Ｈ２ＳＯ４－ＮＨ４Ａｃ介质中，Ｃｏ（Ⅱ）－β－巯基丙酸（ＭＰＡ）－ＮａＮＯ２体系产生－灵敏的极谱催化波，峰电位在－０．８４Ｖ（ｖｓ．ＳＣＥ），钴浓度在０．０２～１００ｎｇ／ｍＬ范围内与峰电流呈线性关系。检出限为０．０１ｎｇ／ｍＬ。本文对极谱波的性质和机理进行了初步探讨。本法用于土壤中总钴和有效钴的测定，结果满意。     

钴（Ⅱ）—β—巯基丙酸—NaNO2体系的极谱化波研究

在ｐＨ３．８的Ｈ２ＳＯ４－ＮＨ４Ａｃ介质中，Ｃｏ（Ⅱ）－β－巯基丙酸（ＭＰＡ）－ＮａＮＯ２体系产生－灵敏的极谱催化波，峰电位在－０．８４Ｖ（ｖｓ．ＳＣＥ）钴浓度在０．０２～１００ｎｇ／ｍＬ范围内与峰电流呈线性关系，检出限为０．０１ｎｇ／ｍＬ。本文对极谱波的性质和机理进行了初步探讨，本法用于土壤中总钴和有效钴的测定，结果满意。     

Simple determination of 22 organophosphorous pesticides in human blood using headspace solid-phase microextraction and gas chromatography with mass spectrometric detection

A simple and rapid procedure for the determination of 22 organophosphorous pesticides (bromophos-ethyl, bromophos-methyl, chlorfenvinphos, chlorpyriphos, demethon-S-methylsulfon, diazinon, dichlorvos, dicrotophos, dimethoate, disulfoton, edifenphos, fenitrothion, fenthion, malathion, methidathion, mevinphos, monocrotophos, omethoate, parathion-ethyl, parathion-methyl, phosphamidon, and quinalphos) in human blood using headspace (HS) solid-phase microextraction (SPME) and gas chromatography (GC)-mass spectrometry (MS) is presented. The effects of various sample additions, incubation temperatures, absorption times, desorption times, and depths of fiber insertion into the injection port of the GC are optimized to enhance the sensitivity of the procedure. The recoveries of spiked blood samples are determined between 70% and 95% compared with samples prepared in water, and absolute recoveries are in the range between 0.1% and 19.6%. For quantitation in the single ion monitoring mode, linearity is established over concentration ranges from 0.025 to 5.0 microg/g with excellent coefficients of correlation (0.991-0.998). The detection limits are in the range between 0.01 and 0.3 microg/g. The time for analysis is 44 min per sample including extraction and GC-MS analysis. HS-SPME in combination with GC-MS is an effective method for the determination of organophosphorous pesticides in human blood and shows a great potential for use in rapid on-site analytical work, which is highly demanded in clinical and forensic toxicology.     

Preconcentration of diazinon using multiwalled carbon nanotubes as solid-phase extraction adsorbents

A sensitive and selective column adsorption method is proposed for the preconcentration and determination of diazinon. Diazinon was preconcentrated on multiwalled carbon nanotubes (MWCNTs) as an adsorbent and then determined by high-performance liquid chromatography (HPLC). Several parameters on the recovery of the analyte were investigated. The experimental results showed that it was possible to obtain quantitative analysis when the solution pH was 6 using 200 mL of validation solution containing 2 μg of diazinon and 5 mL of acetonitrile as an eluent. Recovery of diazinon was 95.2 ± 4.2% with a relative standard deviation for seven determinations of 4.9% under optimum conditions. The maximum preconcentration factor was 200 for diazinon when 1000 mL of sample solution volume was used. The linear range of calibration curve was 0.3 to 10,000 ng mL^− 1 with a correlation coefficient of 0.997 and the detection limit (3S/N) was 0.06 ng mL^− 1. The proposed method was successfully applied to the determination of diazinon in tap water with high precision and accuracy.     

固相微萃取/气相色谱-质谱检测纺织品中有机磷农药残留

采用PDMS萃取纤维一次吸附富集纺织品中马拉硫磷、甲基对硫磷、敌敌畏、三唑磷、对硫磷、喹硫磷、二嗪磷7种有机磷农药,在气相色谱-质谱(GC-MS)进样口热解吸后进行定性定量检测。筛选了几种商品化的萃取纤维,并优化了萃取时间、萃取温度、吸附时间、盐浓度以及pH值等萃取条件。本方法操作简单、快速、环保,检出限低,可适用于生态纺织品中物质的快速检测。     

A novel chemiluminescence assay of organophosphorous pesticide quinalphos residue in vegetable with luminol detection

Background  

Organophosphorous pesticides are the most popular pesticides used in agriculture. As acetylcholinesterase inhibitors, organophosphorous pesticides are toxic organic chemicals. The control and detection of organophosphorous pesticide residue in food, water, and environment therefore plays a very important role in maintaining physical health. A sensitive, rapid, simple chemiluminescence(CL) method has been developed for the determination of quinalphos based on the reaction of quinalphos with luminol-H₂O₂ in an alkaline medium. The method has been applied to detection of quinalphos in vegetable samples with satisfactory results.     

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.     

Determination of eight selected organophosphorus insecticides in postmortem blood samples using solid-phase extraction and gas chromatography/mass spectrometry

A simple, rapid and sensitive method is described for the determination of omethoate, dimethoate, diazinon, chlorpyrifos, parathion‐ethyl, chlorfenvinphos, quinalphos and azinphos‐ethyl in postmortem whole blood samples. The analytes and internal standard (ethion) were isolated from the matrix by solid‐phase extraction, and were analysed by gas chromatography/mass spectrometry in the selected ion monitoring mode. The method has shown to be selective after analysis of postmortem samples of 40 different origins. Calibration curves were established between 0.05 (0.1 for omethoate) and 25 µg/mL, and the values obtained for intra‐ and interday precision and accuracy were within the criteria usually accepted for bioanalytical method validation. Lower limits of quantitation were 50 ng/mL for all compounds, except for omethoate (100 ng/mL); the limits of identification of the method were 25 ng/mL for all analytes, except for omethoate, for which 50 ng/mL was obtained. Absolute recovery was determined at three concentration levels, and ranged from 31 to 108%. The proposed method is simple and fast, and can be routinely applied in the determination of these compounds in postmortem whole blood samples within the scope of forensic toxicology. In addition, mass spectrometry has demonstrated to be a powerful and indispensable tool for the unequivocal identification of the analytes, since the acceptance criteria were accomplished even at very low levels, thus allowing obtaining forensically valid and sound results. Copyright © 2010 John Wiley & Sons, Ltd.     

An Evaluation of High Performance Liquid Chromatography-UV for the Multi-Residue Analysis of Organophosphorous Pesticides in Environmental Water

Abstract

In this study isocratic high performance liquid chromatography in the reversed-phase mode (RP-8 or RP-18 column) with UV-detection (254 nm), was evaluated for the analysis, directly or after extraction, of organophosphorous pesticides in environmental water.

Fifteen pesticides were studied and good resolution was obtained for eight by direct analysis of a multi-residue water sample. Reproducibility in terms of retention times was found to be very good. Linear calibration curves were obtained down to 0.5ng/μL (3 ng injected) with a coefficient of variation near 10%. The limit of quantitation for direct analysis was found to be 0.5mg/L (3ng) in water. However, by extraction with methylene chloride or ethyl acetate and concentration of the extract some of the pesticides could be determined at 0.5 μg/L (ppb) in water.     

Determination of diazinon, chlorpyrifos, and their metabolites in rat plasma and urine by high-performance liquid chromatography

This study reports a simple and rapid high-performance liquid chromatographic (HPLC) method for the determination of the insecticide diazinon (O,O-diethyl-O[2-isopropyl-6-methylpyridimidinyl] phosphorothioate), its metabolites diazoxon (O,O-diethyl-O-2-isopropyl-6-methylpyridimidinyl phosphate) and 2-isopropyl-6-methyl-4-pyrimidinol, the insecticide chlorpyrifos (O,O-diethyl-O[3,5,6-trichloro-2-pyridinyl] phosphorothioate) and its metabolites chlorpyrifos-oxon (O,O-diethyl-O[3,5,6-trichloro-2-pyridinyl] phosphate), and TCP (3,5,6-trichloro-2-pyridinol) in rat plasma and urine samples. The method is based on using C18 Sep-Pak cartridges for solid-phase extraction and HPLC with a reversed-phase C18 column and programmed UV detection ranging between 254 and 280 nm. The compounds are separated using a gradient of 1% to 80% acetonitrile in water (pH 3.0) at a flow rate ranging between 1 and 1.5 mL/min in a period of 16 min. The limits of detection ranged between 50 and 150 ng/mL, and the limits of quantitation were 100 to 200 ng/mL. The average percentage recovery of five spiked plasma samples were 86.3 +/- 8.6, 77.4 +/- 7.0, 82.1 +/- 8.2, 81.8 +/- 8.7, 73.1 +/- 7.4, and 80.3 +/- 8.0 and from urine were 81.8 +/- 7.6, 76.6 +/- 7.1, 81.5 +/- 7.9, 81.8 +/- 7.1, 73.7 +/- 8.6, and 80.7 +/- 7.7 for diazinon, diazoxon, 2-isopropyl-6-methyl-4-pyrimidinol, chlorpyrifos, chlorpyrifos-oxon, and TCP, respectively. The relationship between the peak area and concentration was linear over a range of 200 to 2,000 ng/mL. This method was applied in order to analyze these chemicals and metabolites following dermal administration in rats.     

Simple high-performance liquid chromatographic method for the determination of medroxyprogesterone acetate in human plasma

The high-performance liquid chromatographic (HPLC) method was developed as a simple, reliable alternative to available methods for measuring plasma concentrations of medroxyprogesterone acetate (MPA). The HPLC method has been successfully automated and is suitable for the rapid, inexpensive analysis of large batches of plasma samples. The best approach involves a solvent extraction followed by HPLC separation and analysis. MPA can be efficiently extracted, at all pH values, by nonpolar solvents. The Spherisorb 5-ODS2 HPLC column provides excellent separation of MPA from endogenous steroids of similar structure and from extraneous plasma blank peaks. A batch of 30-40 samples can be prepared by HPLC analysis in 2-3 hours, with a chromatographic run time of 10 minutes/sample. Calibration curves between 5-250 ng/ml show a good correlation between peak height ratio and MPA concentration, even at low levels. Plasma concentrations of MPA in patients receiving 1 g/day were between 12.6-270 ng/ml in this study, suggesting that the sensitivity of this method, 10 ng/ml, is sufficient for monitoring therapeutic concentrations of MPA. The results show a wide individual variation in plasma concentrations following similar dosing schedules--a finding reported by other workers.     

Determination of organophosphorous pesticides in the ppq range using a simple solid-phase extraction method combined with dispersive liquid-liquid microextraction

Solid-phase extraction combined with dispersive liquid-liquid microextraction (SPE-DLLME) was applied for the extraction of six organophosphorous pesticides (OPPs) in water samples. The analytes considered in this study were determined by gas chromatography with mass spectrometry and included prophos, diazinon, chlorpyrifos methyl, methyl parathion, fenchlorphos and chlorpyrifos. Several extraction conditions (extraction solvent and elution/dispersion solvents nature, extraction solvent volume, elution solvent volume, water volume and sample volume) were tested for SPE-DLLME with these analytes and the best results were obtained using carbon tetrachloride as the extraction solvent and acetone as the elution/dispersion solvent. Calibration curves for the determination of OPPs in water samples were constructed in the concentration range of 10-100 ng/L. Limits of detection (LODs) ranged from 38 to 230 pg/L values that are below the maximum admissible level for drinking water (100 ng/L). Relative standard deviations (RSD) were between 8.6 and 10.4% for a fortification level of 100 ng/L. At the same fortification level, the relative recoveries (R.R.) of tap, well and irrigation water samples were in the range of 30.2-97.1%.