阴离子交换固相萃取-气相色谱/质谱法分析人血浆中6种神经性毒剂降解产物

采用醋酸汞去除蛋白,实现了阴离子交换固相萃取-气相色谱/质谱法同时测定人血浆中6种神经性毒剂降解产物的三甲基硅烷衍生物。考察了不同溶剂的去蛋白效率和不同固相萃取柱对毒剂降解产物的保留行为,优化了阴离子交换树脂的洗脱条件。采用选择离子监测方式,6种降解产物在0.05~5.0 mg/L范围内呈良好的线性关系,最低检出限在22μg/L以内;RSD均小于9.7%。该方法检测灵敏度高,血浆样品干扰小,是一种理想的血浆中神经性毒剂降解产物的检测方法。     

尿样中神经性毒剂代谢产物的HPLC/Q-TOFMS/MS检测方法研究

建立了尿样中甲基膦酸单乙酯(EMPA)、甲基膦酸单异丙酯(IMPA)、甲基膦酸频哪基酯(PMPA)3种神经性毒剂代谢产物的HPLC/Q-TOFMS/MS检测方法。以StrataSi-1型固相萃取小柱对尿样中的3种神经性毒剂代谢产物进行分离,HPLC/Q-TOFESIMS/MS进行测定,内标法定量。该方法对EMPA、IMPA、PMPA的线性范围均为5～320μg/L,相关系数均不低于0.9974;EMPA、IMPA、PMPA的加标回收率分别为57%、98%、81%;检出限(S/N≥3)均为0.1μg/L,定量下限(S/N≥10)均为1μg/L。并将该方法应用于禁化武组织(OPCW)首次生物医学样品分析演练未知尿样的检测,结果满意。     

茶叶中7种拟除虫菊酯农药残留的测定

用宽口径弹性石英柱色谱分析法测定了茶叶中7种菊酯类农药残留。试验了样品中农药残留物的提取方法,确定了最佳分析条件。该法最低检出浓度为1．0－5．5μg/kg,样品加标回收率为84．6％－95．0％。     

单扫描极谱法测定果、蔬中有机磷农药残留量

提出了在0．40mol/L氢氧化钠底液中对碱解后的有机磷农药进行单扫描极谱测定的方法。于起始电位－0．30V（vs SCE)进行阴极化扫描时有产生一灵敏导数波,峰电位为－0．53V（vs SCE)。并获得了辛硫磷残留量检测的最佳条件。在此条件下检测有机磷农药的线性范围分别为：辛硫磷0．12－160μg/mL,甲基对硫磷0．5－200μg/mL,水胺硫磷0．20－160μg/mL,甲胺磷0．1－1．0ng/mL,氧化乐果0．09－160μg/mL。     

沙土中5种神经性毒剂降解产物的实时直接分析-质谱法快速检测

建立了实时直接分析离子源-质谱（DART-MS）快速检测沙土中5种神经性毒剂降解产物的方法。方法在0.03～10 mg/L范围内线性关系良好，检出限为0.03～0.1 mg/kg, 5种神经性毒剂降解产物在沙土中的回收率均不低于71.8%，相对标准偏差（RSD）不超过11%。利用建立的DART-MS定性方法分析了禁止化学武器组织（OPCW）的PT48次环境样品水平考试盲样样品，根据获得的母离子和碎片离子的高分辨质谱（HRMS）数据及MS/HRMS质谱碎裂特征，鉴定出所有适合DART-MS分析的化学毒剂相关化合物，与OPCW发布的配样清单一致。     

染毒水样中神经性毒剂水解产物的分析

考察了对水中6种神经性毒剂水解产物固相萃取的萃取剂,洗脱剂等因素对萃取率的影响,以LC－CN小柱为萃取剂,1％冰醋 甲醇溶液为洗脱剂,测得萃取回收率为59．7％－100％,相对标准偏差为1．4％－7．2％,采用气相色谱和色质联用－选择离子检测法对水解产物三甲基硅烷（TMS）衍生物进行分析鉴定,水中水解产物最低检测浓度为0．002－0．02mg/L。为今后水中神经性毒剂未知样品分析提供了简便,快速的分析方法。     

测定尿中痕量碘的高锰酸钾-亚砷酸体系催化光度法

在硫酸和磷酸的介质中,碘离子催化高猛酸钾与亚砷酸反应生成的锰（Ⅲ）氧化砷酸的反应,据此建立了催化光度法测定痕量碘的新方法。该法的检出限为0．4μg/L,测定的线性范围为1．0－25．0μg/L。应用该法测定了尿样中痕量碘的含量,获得了满意的结果,测定样品的相对标准偏差（n＝6）为2．5％－3．7％,加标回收率为96．4％－102．6％。     

流动注射原子吸收光谱法测定富硒天麻、葡萄及大米中的硒

建立了流动注射氢化物发生-原子吸收光谱法测定富硒天麻、葡萄及大米中硒的方法。测定硒的线性范围为0．33μg/L-50μg/L，相对标准偏差小于3％，加标回收率为93％-106％。方法已广泛应用于实际样品中微量硒的测定。     

微波辅助萃取气相色谱-质谱联用测定蔬菜中的扑草净

研究了微波辅助萃取气相色谱．质谱联用测定植物样品中扑草净的方法，比较了几种不同溶剂的微波萃取效率，从而选取二氯甲烷为萃取溶剂，并采用三因素三水平的正交设计试验对溶剂体积、微波辐射时间、微波功率进行了优化。在优化的实验条件下分析了合成菠菜样品，对0．2μg/g和0．02μg/g的合成菠菜样品，回收率分别为99．5％和92．5％，相对标准偏差分别为5．0％和ll％，方法的线性范围为1．0—400ng／g，检出限为0．22ng／g。方法适合于分析植物样品中的扑草净。     

垃圾渗滤液中 As和 Hg的流动注射蒸气发生非色散原子荧光光谱法测定

建立了垃圾渗滤液中As和Hg的流动注射蒸气发生－非色散原子荧光光谱的测定方法。在低温下采用硝酸－过氧化氢体系消化处理样品;硫脲－抗坏血酸将As(V）还原后测定样品中的总As;Hg的测定用Hg蒸气发生原子荧光光谱法。对测量条件进行了优化,在优化实验条件下测得As和Hg的检出限分别为0．08和0．007μg/L,10次测定的相对标准偏差分别为0．48％和0．85％（对8．0μg/L As和1．0μg/L Hg标准溶液）。共存的NaCI、MgCI2、CaCI2、Na2SO4、NaF以及微量共存金属离子（Cd、Se、Zn、Pb、Cu、Fe、Mn、AI）对As和Hg的测定没有干扰。用标准校正曲线和标准加入法对样品测定结果进行了比较,实验结果表明二者吻合较好。     

Ultrasound-assisted emulsification-microextraction coupled to ion mobility spectrometry for monitoring of atrazine and simazine in environmental water

Triazine herbicides and some of their transformation products are considered as one of the most important classes of chemical pollutants owing to their widespread use and toxicity. Triazines and their degradation products have caused concern because they are toxic and persistent in water, soil, and organisms. The present paper describes the validation of ultrasound-assisted emulsification-microextraction (USAEME) method for determination of atrazine and simazine using ion mobility spectrometry (IMS) in environmental water. The parameters influencing the extraction efficiency such as sonication time, extraction solvent, extraction volume and salt concentration were investigated. Under the optimum conditions, enrichment factors was 170 and 150 with corresponding LOD of 8 and 12 μg/L for atrazine and simazine respectively . Linearity with a coefficient of estimation (r²) were >0.99 in the concentration level range of 15–1500 μg/L and 20–1700 μg/L for extraction of atrazine and simazine in water samples. The proposed method successfully was applied to screen of atrazine and simazine in environmental water.     

Determination of glyoxal,methylglyoxal, and diacetyl in red ginseng products using dispersive liquid–liquid microextraction coupled with GC–MS

A simple and rapid dispersive liquid–liquid microextraction method coupled with gas chromatography and mass spectrometry was applied for the determination of glyoxal as quinoxaline, methylglyoxal as 2‐methylquinoxaline, and diacetyl as 2,3‐dimethylquinoxaline in red ginseng products. The performance of the proposed method was evaluated under optimum extraction conditions (extraction solvent: chloroform 100 μL, disperser solvent: methanol 200 μL, derivatizing agent concentration: 5 g/L, reaction time: 1 h, and no addition of salt). The limit of detection and limit of quantitation were 1.30 and 4.33 μg/L for glyoxal, 1.86 and 6.20 μg/L for methylglyoxal, and 1.45 and 4.82 μg/L for diacetyl. The intra‐ and interday relative standard deviations were <4.95 and 5.80%, respectively. The relative recoveries were 92.4–103.9% in red ginseng concentrate and 99.4–110.7% in juice samples. Red ginseng concentrates were found to contain 191–4274 μg/kg of glyoxal, 1336–4798 μg/kg of methylglyoxal, and 0–830 μg/kg of diacetyl, whereas for red ginseng juices, the respective concentrations were 72–865, 69–3613, and 6–344 μg/L.     

Rapid screening of precursor and degradation products of chemical warfare agents in soil by solid-phase microextraction ion mobility spectrometry (SPME-IMS)

The use of solid-phase microextraction (SPME) coupled to ion mobility spectrometry (IMS) to detect precursor and degradation products of chemical warfare agents (CWAs) as soil contaminants was investigated. The development and characterization of a system to interface a thermal desorption solid-phase microextraction inlet with a hand held ion mobility spectrometer was demonstrated. The analytes used in this study were diisopropyl methylphosphonate (DIMP), diethyl methylphosphonate (DEMP), and dimethyl methylphosphonate (DMMP). Two SPME fibers with different stationary phases, 100 μm polydimethylsiloxane (PDMS) and 65 μm polydimethylsiloxane divinylbenzene (PDMS/DVB), were evaluated in this study to determine the optimal fiber and extraction conditions. Better results were obtained with the PDMS fiber. SPME-IMS offered good repeatability and detection of the precursor and degradation products in spiked soil at concentrations as low as 10 μg/g. Sample analysis time was less than 30 min for all the precursor and degradation products.     

Determination of degradation products of chemical warfare agents in water using hollow fibre-protected liquid-phase microextraction with in-situ derivatisation followed by gas chromatography-mass spectrometry

Hollow fibre-protected liquid-phase microextraction (HF-LPME) together with gas chromatography/mass spectrometry was investigated for the analysis of degradation products of chemical warfare agents in water samples. The degradation products studied were those of nerve and blister agents, and a psychotomimetic agent. Extractions were successfully performed coupled with in-situ derivatisation using a mixture of solvent and derivatising agent. The protection of the moisture-sensitive derivatising agent was afforded by the hollow fibre. Parameters such as extraction solvent, pH, salt concentration, stirring speed and extraction time were optimised using spiked deionised water samples. The linear range established was between 0.005 and 5 microg ml(-1) depending on analyte, with squared regression coefficients ranging from 0.9929 to 1.0000. Relative standard deviations ranged from 9% to 22%. As compared to those of solid-phase microextraction, the limits of detection (0.01-0.54 microg l(-1)) of the newly-developed approach were significantly improved.     

Selective enrichment of the degradation products of organophosphorus nerve agents by zirconia based solid-phase extraction

Selective extraction and enrichment of nerve agent degradation products has been achieved using zirconia based commercial solid-phase extraction cartridges. Target analytes were O-alkyl alkylphosphonic acids and alkylphosphonic acids, the environmental markers of nerve agents such as sarin, soman and VX. Critical extraction parameters such as modifier concentration, nature and volume of washing and eluting solvents were investigated. Amongst other anionic compounds, selectivity in extraction was observed for organophosphorus compounds. Recoveries of analytes were determined by GC-MS which ranged from 80% to 115%. Comparison of zirconia based solid-phase extraction method with anion-exchange solid-phase extraction revealed its selectivity towards phosphonic acids. The limits of detection (LOD) and limit of quantification (LOQ) with selected analytes were achieved down to 4.3 and 8.5 ng mL(-1), respectively, in selected ion monitoring mode.     

Analysis of Malathion pesticide residues in rice samples using ultrasound-assisted emulsification-microextraction coupled to UV photoionization source ion mobility spectrometry

The present paper describes the validation of ultrasound-assisted emulsification-microextraction method followed by ion mobility spectrometry (IMS) for determination malathion pesticides. Ultrasound radiation was applied for accelerating the emulsification of microliter organic solvent in aqueous solutions and enhancing the microextraction efficiency. This preconcentration step combined with IMS detection provided a precise and accurate method for determination of trace amounts of malathion pesticides. The effect of parameters influencing the extraction efficiency such as sonication time, type of extraction solvent, extraction solvent volume, and salt concentration were investigated and discussed. Under the optimum conditions, enrichment factors was 270 with corresponding LOD of 4 μg/L. Linearity with a coefficient of estimation (r²) were >0.99 in the concentration level range of 6–750 μg/L for extraction of Malathion in water samples. The applicability of the proposed method was evaluated by determination of the residues of the investigated pesticide in rice paddy water gathered from four stations during 60 days after spraying (June 2014), and in storage rice samples in Mazandaran province, Iran.     

Determination of nerve agent degradation products by capillary electrophoresis using field-amplified sample stacking injection with the electroosmotic flow pump and contactless conductivity detection

In the present study, field-amplified sample stacking injection using the electroosmotic flow pump (FAEP) was developed for the capillary electrophoretic separation of the four nerve agent degradation products methylphosphonic acid (MPA), ethyl methylphosphonic acid (EMPA), isopropyl methylphosphonic acid (IMPA) and cyclohexyl methylphosphonic acid (CMPA). Coupled to contactless conductivity detection, direct quantification of these non-UV active compounds could be achieved. Sensitivity enhancement of up to 500 to 750-fold could be obtained. The newly established approach was applied to the determination of the analytes in river water and aqueous extracts of soil. Detection limits of 0.5, 0.7, 1.4 and 2.7 ng/mL were obtained for MPA, EMPA, IMPA and CMPA, respectively, in river water and 0.09, 0.14, 0.44 and 0.22 μg/g, respectively, in soil.     

Simultaneous derivatization and air‐assisted liquid–liquid microextraction of some parabens in personal care products and their determination by GC with flame ionization detection

A simultaneous derivatization/air‐assisted liquid–liquid microextraction technique has been developed for the sample pretreatment of some parabens in aqueous samples. The analytes were derivatized and extracted simultaneously by a fast reaction/extraction with butylchloroformate (derivatization agent/extraction solvent) from the aqueous samples and then analyzed by GC with flame ionization detection. The effect of catalyst type and volume, derivatization agent/extraction solvent volume, ionic strength of aqueous solution, pH, numbers of extraction, aqueous sample volume, etc. on the method efficiency was investigated. Calibration graphs were linear in the range of 2–5000 μg/L with squared correlation coefficients >0.990. Enhancement factors and enrichment factors ranged from 1535 to 1941 and 268 to 343, respectively. Detection limits were obtained in the range of 0.41–0.62 μg/L. The RSDs for the extraction and determination of 250 μg/L of each paraben were <4.9% (n = 6). In this method, the derivatization agent and extraction solvent were the same and there is no need for a dispersive solvent, which is common in a traditional dispersive liquid–liquid microextraction technique. Furthermore, the sample preparation time is very short.     

Dispersive liquid–liquid microextraction with in situ derivatization coupled with gas chromatography and mass spectrometry for the determination of 4‐methylimidazole in red ginseng products containing caramel colors

A rapid analytical method was developed for the determination of 4‐methylimidazole from red ginseng products containing caramel colors by using dispersive liquid–liquid microextraction with in situ derivatization followed by gas chromatography with mass spectrometry. Chloroform and acetonitrile were selected as the extraction and dispersive solvents, and based on the extraction efficiency, their optimum volumes were 200 and 100 μL, respectively. The optimum volumes of the derivatizing agent (isobutyl chloroformate) and catalyst (pyridine), pH, and concentration of NaCl in the sample solution were determined to be 25 and 100 μL, pH 7.6, and 0% w/v, respectively. Validation of the optimized method showed good linearity (R² > 0.999), accuracy (≥89.86%), intra‐ (≤6.70%) and interday (≤4.17%) repeatability, limit of detection (0.96 μg/L), and limit of quantification (5.79 μg/L). The validated method was applied to quantify 4‐methylimidazole in red ginseng juices and concentrates, 4‐methylimidazole was only found in red ginseng juices containing caramel colorant (42.91–2863.4 μg/L) and detected in red ginseng concentrates containing >1% caramel colorant.     

Determination of lewisite constituents in aqueous samples using hollow-fibre liquid-phase microextraction followed by gas chromatography-mass spectrometry

The applicability of hollow-fibre liquid-phase microextraction for extracting 2-chlorovinyldichloroarsine (lewisite 1), bis(2-chlorovinyl)chloroarsine (lewisite 2), tris(2-chlorovinyl)arsine (lewisite 3) and arsenic trichloride from aqueous samples is reported. Parameters affecting the extraction efficiency of these chemicals were optimised. These parameters included the type of derivatising agent, extraction solvent, derivatisation method, pH, ionic strength, stirring speed and extraction time. A linear range between 0.002 and 0.2 μg/mL was established for the lewisites with good square regression coefficients (0.9955–0.9992). Good reproducibility with relative standard deviations (RSDs) from 8 to 10 % was achieved. The limit of detection was 0.002 μg/mL for the lewisites and 0.005 μg/mL for arsenic trichloride (3:1 signal-to-noise ratio). The extraction method was validated with a proficiency test sample issued by the Organisation for the Prohibition of Chemical Weapons (OPCW). The rapidity and precision of the new method should help deter against the employment of lewisite as a chemical warfare agent: its use could be confirmed easily from analysis of aqueous samples.