分散液液微萃取-衍生化高效液相色谱-荧光检测法测定环境水样中4种酚类内分泌干扰物

为实现小体积环境水样中酚类化合物的准确、快速、高灵敏测定,通过分散液液微萃取(DLLME)和荧光衍生化的结合,建立了高效液相色谱-荧光检测(HPLC-FLD)双酚A、壬基酚、辛基酚和对特辛基酚的分析方法。考察并优化了DLLME和衍生化条件,结果表明,最优的DLLME条件为萃取剂氯仿用量70μL,分散剂乙腈用量400μL,漩涡振荡3 min,高速离心2 min。以2-[2-(7 H-二苯并[a,g]咔唑-乙氧基)]-乙基氯甲酸酯(DBCEC-Cl)为柱前衍生试剂,在pH10.5的Na2CO3-NaHCO3缓冲液/乙腈溶液、50℃下衍生反应3 min得到稳定的衍生产物,于10min内实现了4种酚衍生物的分离。方法的检出限为0.9~1.6 ng/L,定量限为3.8~7.1 ng/L,具有良好的线性、精密度和回收率,与以往报道的方法相比具有一定的优势和实用性,可用于造纸厂废水、湖水、生活废水、自来水中4种酚类内分泌干扰物的测定。     

金属-有机纳米管分散固相萃取-气相色谱-串联质谱高灵敏分析环境水样中痕量多氯联苯

采用含铅金属-有机纳米管为吸附剂,基于分散固相萃取和气相色谱-串联质谱建立了一种高灵敏分析环境水样中痕量多氯联苯的方法.采用正交设计响应面法对影响萃取效果的重要因素(如离子强度、萃取时间和吸附剂用量等)进行了优化.获得的最优条件为:离子强度4.92 %(w/V)NaCl,萃取时间4.5 min,正己烷为解吸剂,吸附剂用量62.5 mg.在优化条件下,方法的线性范围为2~1000 ng/L,检出限为0.26~0.82 ng/L. 日内和日间相对标准偏差分别为0.8%~5.5% (200 ng/L, n=6)和2.7%~7.4% (200 ng/L, n=6).将本方法应用于实际环境水样中多氯联苯的分析,回收率为78.9%~113.3%,结果满意.     

毛细管电泳-激光诱导荧光法测定草甘膦、草胺膦及氨甲基膦酸

建立了一种快速、有效的毛细管电泳分离-激光诱导荧光检测有机磷除草剂草甘膦、草胺膦和草甘膦的代谢物氨甲基膦酸的方法。将荧光衍生试剂5-(4, 6-二氯三嗪基)氨基荧光素(DTAF)成功用于衍生上述3种化合物。最佳衍生条件: DTAF的浓度为1.0 μmol/L,以50 mmol/L硼酸(pH 9.5)作为缓冲溶液,在30 ℃下反应40 min。以pH 9.5的30 mmol/L硼酸缓冲溶液(含15 mmol/L Brij-35)作为电泳背景电解质,3种衍生物得到基线分离。在优化的条件下,草甘膦、草胺膦、氨甲基膦酸的检出限分别为3.21、6.14和1.99 ng/kg。将该方法应用于环境水样和土壤中除草剂及代谢物的测定,回收率为91.3%～106.0%。该方法准确、灵敏,可满足环境样品中有机磷农药及其代谢物残留的检测要求。     

手性荧光衍生化反相高效液相色谱法分析多巴胺

以R(-)_4_(N,N_Dimethylaminosulfonyl)_7_(3_isothiocyanatopyrrolidino)_2,1,3_benzoxadiazole(R(-)_DBD_PyNCS)作为手性荧光衍生化试剂, 用反相高效液相色谱法(RP-HPLC)定量分析多巴胺。衍生化反应是在含有7%吡啶溶剂中, 75 ℃温度条件下, 进行40 min, 生成具有荧光特性的多巴胺衍生物(λex= 460 nm, λem= 550nm)。生成的衍生物在流动相为乙腈-水(体积比35∶65), 流速为1.0 mL/min, 在DiamonsilTM C18(150 mm×4.6mm, i.d., 5μm)色谱柱上保留时间约为15 min。多巴胺衍生物在60~1 200 ng/mL时与峰面积呈良好的线性关系(r=0.999 6), 多巴胺浓度为1 mmol/L时, 峰面积测定结果的相对标准偏差(RSD)为2.4%, 检出限为12 ng/L(S/N=3)。检测了盐酸多巴胺注射液中多巴胺的含量。     

氟化共价有机聚合物固相微萃取-高效液相色谱测定水产品中丁香酚类麻醉剂

氟化共价有机聚合物(F-COP)具有较大的比表面积和吸附容量,对丁香酚类化合物具有特异性吸附。该文以2,3,5,6-四氟对二苯甲醛(TFA)和1,3,5-三(4-氨苯基)苯(TAPB)为单体,三氟甲磺酸钪(Sc(OTf)₃)为催化剂在室温下快速合成F-COP,并将其作为固相微萃取(SPME)吸附剂,结合高效液相色谱-紫外检测法(HPLC-UV),建立了测定水产品中丁香酚、乙酸丁香酚酯和甲基丁香酚麻醉剂的分析方法。通过傅里叶红外光谱、X射线衍射、N₂吸附-解吸等温线和扫描电子显微镜等手段对F-COP材料进行表征。考察了萃取时间、搅拌速度、解吸溶剂及解吸时间对丁香酚类麻醉剂萃取量的影响,在萃取时间为30 min、搅拌速度为700 r/min、解吸溶剂为乙腈、解吸时间为10 min时,丁香酚类麻醉剂获得了最佳的萃取效果。在Diamonsil Plus C₁₈-B色谱柱(250 mm×4.6 mm, 5 μm)上,以甲醇-水(60∶40, v/v)为流动相,流速0.800 mL/min,进样量20.0 μL,紫外检测波长280 nm,柱温30 ℃条件下,丁香酚和乙酸丁香酚酯在10~1000 μg/L,甲基丁香酚在10~1500 μg/L范围内呈现出良好的线性关系,相关系数(r²)大于0.9961,方法检出限为2.9~4.5 μg/kg(S/N=3),精密度小于8.7%(n=5)。最后,将该分析方法用于罗非鱼和基围虾样品的3种麻醉剂残留分析中,得到了满意的回收率(76.7%~104%)。结果表明,F-COP-SPME-HPLC-UV可满足水产品中丁香酚类麻醉剂的分析检测。     

同位素编码衍生-分散液液微萃取/超高效液相色谱-串联质谱检测大鼠脑微透析液中儿茶酚胺

为实现微量大鼠脑微透析液中3种儿茶酚胺化合物的高灵敏检测,采用d0/d3-10-甲基-吖啶酮-2-磺酰氯(d0/d3-MASC)为同位素编码衍生化试剂,联合使用超声辅助分散液液微萃取技术,建立了超高效液相色谱-串联质谱(UHPLC-MS/MS)快速测定多巴胺(DA)、肾上腺素(EP)和去甲肾上腺素(NE)的分析方法。分别以d0-MASC和d3-MASC衍生微透析液样品和对照品,混合后采用分散液液微萃取技术富集净化,再进行UHPLC-MS/MS检测,以d3-MASC衍生物作为相应d0-MASC衍生物的内标物进行定量。结果表明,在p H 10.8乙腈水溶液中于37℃衍生反应3 min,即可实现待测物的完全分离与检测,3种儿茶酚胺化合物的线性范围为0.02~10.0 nmol/L,相关系数大于0.995,检出限为0.005~0.010 nmol/L,定量下限为0.018~0.040 nmol/L。该方法与已报道方法相比具有显著优势,能够满足大鼠脑微透析液中儿茶酚胺的检测要求。     

气相色谱-质谱法测定水体中5种典型有机紫外防晒剂

建立了水体中5种典型有机紫外防晒剂甲氧基肉桂酸乙基己酯（ethylhexyl methoxycinnamate,EHMC）、二苯酮-3（benzophenone-3,BP-3）、4-甲基苄亚基樟脑（4-methylbenzylidene camphor,4-MBC）、奥克立林（octocrylene,OC）和胡莫柳酯（homosalate,HMS）的气相色谱-质谱检测方法。对HMS、BP-3衍生化条件进行了系统的优化。以100 μL双（三甲基硅烷基）三氟乙酰胺（N,O-bis（trimethylsilyl） trifluoroacetamide,BSTFA）为衍生化试剂,在100 ℃下反应100 min。水样固相萃取选用Oasis HLB萃取柱（0.5 g）,洗脱溶剂为乙酸乙酯-二氯甲烷（1：1,v/v）,水样pH 3~5。该方法对5种化合物的检出限范围为0.5~1.2 ng/L,定量限范围为1.4~4.0 ng/L。最佳实验条件下,加标水样回收率为87.85%~102.34%,相对标准偏差（n=3）均小于5%。该方法成功地应用于昆明市第一污水厂进出口水样中目标物质的分析。     

顶空固相微萃取-气相色谱-质谱测定水中异味化合物

采用顶空固相微萃取-气相色盐／质谱联用测定了水中常见的3种异味化合物，即2-甲基异茨醇、土腥素和β-柠檬醛。研究并讨论了纤维头的类型、盐的种类和浓度、温度、萃取时间、搅拌和解吸时间等因素对异味化合物萃取量的影响。结果表明：在水样中加入30％（W／V）的NaCl溶液，采用65μm PDMS／DVB纤维头，在搅拌的条件下，于60℃顶空萃取40min为异味化合物固相微萃取的最佳条件。在优化的条件下，使异味化合物吸附于纤维涂层后，将其在250℃高温下解吸，再用GC—MS分析。土腥素、β-柠檬醛、2-甲基异茨醇的检出限依次为1．0、1．3和1．7ng／L；其相对标准偏差分别为4．9％、8．4％和6．2％：3种异味化合物在5～1000ng／L的范围内线性关系良好，相关系数均大于0．997。因此，用该方法分析水中痕量（ng／L级）的异味化合物，结果满意。     

毛细管电泳分离-激光诱导荧光检测生物胺

采用新合成的6-氧-[(1-琥珀酰亚胺)氧酰甲基]-荧光素乙酯(SOFE)作为柱前衍生试剂,毛细管电泳分离-激光诱导荧光检测了乙醇胺(EOA)、组胺(His)、甲胺(MA)、乙胺(EA)、酪胺(TYR)及苯乙胺(PEA)6种生物胺。在硼酸-硼砂缓冲溶液(pH8.5)中,室温(25℃)下衍生10min。用pH8.5的含25mmol/LSDS15%(V/V)乙腈的40mmol/L硼酸盐溶液作为电泳缓冲溶液,6种衍生物在15min内完全分离,检出限在2.5×10-11～8×10-11mol/L之间。该方法应用于酱油中生物胺的测定,结果令人满意。     

基于Ti_(3)C_(2)T_(x)/聚酰亚胺复合材料的分散固相萃取-液相色谱法测定尿液中儿茶酚胺类神经递质北大核心CSCD

研究通过一种快速、简便的方法制备了聚酰亚胺功能化的二维碳化钛复合材料Ti_(3)C_(2)T_(x),并用作分散固相萃取吸附剂,结合液相色谱-荧光分析方法对尿液样品中痕量儿茶酚胺类神经递质(CAs)进行分离和分析。利用多种手段对Ti_(3)C_(2)T_(x)/聚酰亚胺的形貌、性质等进行了表征,并详细考察了萃取参数对Ti_(3)C_(2)T_(x)/聚酰亚胺萃取儿茶酚胺类神经递质的萃取性能的影响,结果表明,该复合材料可以通过静电、π-π和氢键作用有效富集目标化合物。最佳萃取条件如下:吸附剂用量为20 mg、样品pH为8.0、吸附时间和脱附时间分别为10 min和15 min、解吸溶剂为醋酸-乙腈-水(5∶47.5∶47.5,v/v/v)。将Ti_(3)C_(2)T_(x)/聚酰亚胺用作分散固相萃取吸附剂与HPLC-FLD联用,建立了一种尿液中CAs的灵敏检测方法,实现了4种CAs物质的定量分析。在最优的条件下,该方法中去甲肾上腺素、肾上腺素、多巴胺和异丙肾上腺素的线性范围为1~250 ng/mL,相关系数(r^(2))均大于0.99,检出限LOD(S/N=3)在0.20~0.32 ng/mL之间,定量限LOQ(S/N=10)在0.7~1.0 ng/mL之间,日内精密度相对标准偏差(RSD)在0.7%~1.09%之间,日间精密度相对标准偏差(RSD)在1.73%~4.24%之间,在实际样品中的加标回收率在82.50%~96.85%之间,精密度RSD的范围在2.47%~9.96%之间。基于Ti_(3)C_(2)T_(x)/聚酰亚胺的分散固相萃取-液相色谱法具有萃取速度快、灵敏度高等特点,可以成功用于尿液中CAs的检测分析。     

磁性分散固相萃取气相色谱法测定地表水中硝基苯类

建立了一种磁性分散固相萃取气相色谱法快速测定地表水中硝基苯类化合物的分析方法,并优化了磁性萃取材料的用量、萃取的时间、解吸溶剂的选择、盐效应等试验影响因素.试验结果表明,硝基苯类化合物的检出限为0.000 4~0.007 mg/L,回收率为84.0%~97.6%,相对标准偏差为3.4%~5.3%.方法具有适用性广、溶剂用量少和操作简便等特点,能很好的测定地表水中的硝基苯类化合物.     

磁性氧化石墨烯固相萃取/高效液相色谱-串联质谱法测定环境水样中6种三嗪类除草剂残留

采用一步合成法制备磁性氧化石墨烯材料(GO-Fe_3O_4),将其用作磁性固相吸附剂对环境水样中的6种三嗪类除草剂进行萃取和富集,并与高效液相色谱-串联质谱法相结合进行测定。以扫描电镜和傅立叶红外光谱对合成材料进行了表征,并考察了GO-Fe_3O_4用量、萃取时间、水样的pH值及离子强度和解吸条件等因素对萃取效率的影响。6种三嗪类除草剂的检出限为0.1~1.0 ng/L,富集倍数可达616~902倍。将方法应用于苏州地区太湖水、运河水和护城河水等实际水样的分析,加标回收率为85.4%~117.6%,相对标准偏差为1.2%~10.0%。该方法操作简单快速,富集倍数较高,检出限低,可用于水样中痕量三嗪类除草剂残留的检测。     

Determination of organophosphorus pesticides by gas chromatography with mass spectrometry using a large‐volume injection technique after magnetic extraction

A fast and efficient method was developed for the extraction and determination of organophosphorus pesticides in water samples. Organophosphorus pesticides were extracted by solid‐phase extraction using magnetic multi‐walled carbon nanotubes and determined by gas chromatography with ion‐trap mass spectrometry. Parameters affecting the extraction were investigated. Under optimum conditions of the method, 10 mg magnetic multi‐walled carbon nanotubes were added into 10 mL sample. After 2 min, adsorbent particles settled at the bottom of test tube with a magnet. After removing aqueous supernatant, the analytes were desorbed with acetonitrile. Then, 70 μL of acetonitrile phase was injected into the gas chromatography and mass spectrometry system that had an ion‐trap analyzer. To achieve high sensitivity, the large‐volume‐injection technique was used with a programmed temperature vaporization inlet, and the ion‐trap mass spectrometer was operated in single ion storage mode. Under the best conditions, the enrichment factors and extraction recoveries were in the range of 113–124 and 74–103%, respectively. The limits of detection were between 3 and 15 ng/L, and the relative standard deviations were < 10%. This method was successfully used for the determination of organophosphorus pesticides in dam water, lagoon water, and river water samples with good reproducibility and recovery.     

MIL-53(Fe)@聚多巴胺@Fe_3O_4磁性复合材料的制备及其用于环境水样中磺酰脲类除草剂的磁固相萃取

制备了MIL-53(Fe)和聚多巴胺(PDA)修饰的磁性Fe_3O_4复合材料MIL-53(Fe)@PDA@Fe_3O_4,并将其作为吸附剂用于磁固相萃取-高效液相色谱法(MSPE-HPLC)检测环境水样中4种磺酰脲类除草剂(甲嘧磺隆、苄嘧磺隆、吡嘧磺隆和氯嘧磺隆)。实验优化了高效液相色谱条件(乙腈和含0.01%(体积分数)三氟乙酸的水溶液为流动相进行梯度洗脱,检测波长为233 nm)及磁固相萃取条件(洗脱剂为5 mL丙酮,萃取时间为4.5 min,吸附剂用量为60 mg,NaCl加入量为0.5 g,溶液pH值为3),在最佳条件下进行方法学考察,4种磺酰脲类除草剂均得到良好的线性关系,相关系数(r)≥0.998 0。方法的检出限(LOD,S/N=3)为0.28~0.77μg/L。将建立的方法用于3种环境水样中4种磺酰脲类除草剂的检测,其加标回收率为78.8%~109.7%。结果表明,制备的功能化复合材料结合了MIL-53(Fe)和Fe_3O_4的优点,可以简便快速地萃取分离环境水样中磺酰脲类除草剂。     

Full automatic determination of chlorophenols in water using solid-phase microextraction/on-fiber derivatization and gas chromatography-mass spectrometry

A fully automated combination of solid-phase microextraction and on-fiber derivatization coupled with gas chromatography-mass spectrometry was developed to determine 17 chlorophenols in aqueous samples. Optimal parameters for the automated process, such as fiber coating (polyacrylate), derivatization reagent (N,O-bis(trimethylsilyl) trifluoroacetamide), extraction time (60 min), derivatization time (5 min), incubation temperature (35°C), sample pH (3), and ionic strength (300 g L(-1) of NaCl), as well as desorption time (5 min) and desorption temperature (270°C) were established. The whole procedure took only 90 min and was performed automatically. The shortcomings of silylation derivatives, like incompleteness and instability, were overcome by using solid-phase microextraction on-fiber silylation in this study. The results from both pure water and river water samples showed that the method had a good linearity (r(2) = 0.9993-1.0000), ranging from 0.01 to 100 μg L(-1). The related standard deviations were between 3.6 and 10.0%. The limits of detections and qualifications ranged from 0.03 to 3.11 ng L(-1) and 0.09 to 10.4 ng L(-1) for the CPs, respectively. The proposed method is superior to traditional solid phase extraction procedure.     

The use of graphene-based magnetic nanoparticles as adsorbent for the extraction of triazole fungicides from environmental water

A graphene-based magnetic nanocomposite (graphene-ferriferrous oxide; G-Fe(3) O(4) ) was synthesized and used as an effective adsorbent for the preconcentration of some triazole fungicides (myclobutanil, tebuconazole, and hexaconazole) in environmental water samples prior to high-performance liquid chromatography-ultraviolet detection. The method, which takes the advantages of both nanoparticle adsorption and magnetic phase separation from the sample solution, could avoid the time-consuming experimental procedures commonly involved in the traditional solid phase extraction such as centrifugation and filtrations. Various experimental parameters affecting the extraction efficiencies such as the amount of the magnetic nanocomposite, extraction time, the pH values of the sample solution, salt concentration, and desorption conditions were investigated. Under the optimum conditions, the enrichment factors of the method for the three analytes were 5824, 3600, and 4761, respectively. A good linearity was observed in the range of 0.1-50 ng/mL for tebuconazole and 0.05-50 ng/mL for myclobutanil and hexaconazole, respectively, with the correlation coefficients ranging from 0.9992 to 0.9996. The limits of detection (S/N = 3) of the method were between 0.005 and 0.01 ng/mL. The results indicated that as a magnetic solid-phase extraction adsorbent, the graphene-ferriferrous oxide (G-Fe(3) O(4) ) has a great potential for the preconcentration of some compounds from liquid samples.     

Ionic liquid-modified magnetic polymeric microspheres as dispersive solid phase extraction adsorbent: a separation strategy applied to the screening of sulfamonomethoxine and sulfachloropyrazine from urine

Ionic liquid-modified magnetic polymeric microspheres (ILMPM) were prepared based on Fe₃O₄ magnetic nanoparticles (MNPs) and ionic liquids (ILs) incorporated into a polymer. The composites were characterized using scanning electron microscopy, Fourier transform infrared analysis, thermogravimetric analysis, X-ray diffraction, and vibrating magnetometer, which indicated that ILMPM had a regularly spherical shape and strong magnetic property. The obtained ILMPM were successfully applied as a special adsorbent of magnetic dispersive solid phase extraction (MDSPE) for the rapid extraction and isolation of sulfamonomethoxine sodium and sulfachloropyrazine sodium in urine. The factors that affected extraction efficiency, such as adsorption conditions, desorption conditions, washing and elution solvents, and pH of the sample solution, were optimized. Under the optimum condition, good linearity in the range of 0.005–2.0 μg g^?1 (r?≥?0.9996) was obtained for the two sulfonamides (SAs); the average recoveries at three spiked levels ranged from 86.9 to 102.1 %, with relative standard deviations of ≤4.3 %. The presented ILMPM-MDSPE method combined the advantages of ILs, MNPs, and MDSPE and therefore could be potentially applied for rapid screening of SAs in urine.     

咔唑-9-乙基氯甲酸酯柱前衍生氨基酸胶束电动色谱分离

采用一种新型紫外、荧光衍生试剂咔唑-9-乙基氯甲酸酯对9种氨基酸(丝氨酸、苏氨酸、甘氨酸、谷氨酸、天冬氨酸、缬氨酸、异亮氨酸、亮氨酸、苯丙氨酸)进行柱前衍生,采用胶束电动色谱模式在14 min内完成分离。分离条件：以pH 9.0的 20 mmol/L硼酸盐-30 mmol/L十二烷基硫酸钠(SDS)溶液（含3%(体积分数)乙腈)为缓冲溶液,柱温25 ℃,分离电压18 kV,紫外检测波长214 nm。该方法的线性范围为0.025~0.25 mmol/L,检出限为2.15~2.46 μmol/L。