分散液-液微萃取/高效液相色谱法测定水样中的痕量双酚A

建立了分散液-液微萃取与高效液相色谱联用技术测定水样中痕量双酚A(BPA)的方法. 通过对实验条件的筛选及优化, 得到最佳条件: 22.5 μL氯苯作萃取剂、0.5 mL丙酮作分散剂、0 min静止萃取时间、调节pH 3.2左右、10%离子强度及9 mL水样体积. 此条件下方法的线性范围为0.5~100 μg/L(R2=0.9941), 检出限为0.10 μg/L. 在BPA质量浓度为1 μg/L条件下, 方法回收率为87.8%~111.0%, 相对标准偏差8.3%(n=5), 富集倍数范围1905~2527. 对添加不同BPA浓度的自来水、地表水及回用中水进行分析, 回收率分别为(108±11.1)%, (107±13.2)%及(81.2±6.2)%(n=3). 在既定的色谱条件下, BPA的测定不受乙炔基雌二醇、雌二醇、雌三醇、雌酮和壬基酚等雌激素的干扰.     

水产品中螺旋霉素、替米考星、泰乐菌素与北里霉素残留量的超高效液相色谱-紫外检测法同时测定

建立了水产品肌肉组织中螺旋霉素、替米考星、泰乐菌素、北里霉素同时测定的超高效液相色谱-紫外检测(UPLC-TUV)方法。样品经乙腈提取后,浓缩至近干,用4%NaCl溶解残渣,正己烷除脂,经固相萃取小柱净化,乙腈洗脱;以乙腈-25 mmol/L磷酸二氢铵(pH2.5,含10%乙腈)为流动相,以ACQUITYUPLC BEHC18为分离柱,柱温为45℃,流速为0.3 mL/min,紫外检测。方法在0.100~20.0 mg/L范围内呈线性相关,螺旋霉素、替米考星、泰乐菌素和北里霉素的相关系数分别为0.998 7、0.999 3、0.999 4和0.998 0。平均回收率为70%~102%,相对标准偏差为2.9%~11.2%,螺旋霉素、替米考星、泰乐菌素和北里霉素的检出限分别为25、25、50、75μg/kg。方法满足水产品肌肉组织中螺旋霉素、替米考星、泰乐菌素和北里霉素的残留量测定。     

高效液相色谱法同步检测牛奶中替米考星、泰乐菌素和螺旋霉素残留量

研究了牛奶中替米考星、泰乐菌素和螺旋霉素残留量的液相色谱同步测定方法。方法采用ZORBAX Eclipse XDB C18(5μm,150 mm×4.6 mmi.d)反相色谱柱,以甲醇为提取液,以SCX因相萃取柱为净化柱,流动相为0.05 mol/L磷酸二氢钠溶液 乙腈,梯度洗脱,流速1 mL/min,用二极管阵列检测器检测,替米考星和泰乐菌素的检测波长285 nm,螺旋霉素的检测波长232 nm,进样量100μL。替米考星、泰乐菌素和螺旋霉素的检出限分别为:30、20、40μg/kg,线性范围为20~800μg/kg,加标回收率为88.8%~99.4%,相对标准偏差为2.2%~8.9%。方法适用于牛奶中替米考星、泰乐菌素和螺旋霉素残留量的同步检测。     

气相色谱-串联质谱法测定螺旋霉素中的N-亚硝基二甲胺

采用气相色谱-串联质谱法(GC-MS/MS),建立了螺旋霉素原料药中N-亚硝基二甲胺(NDMA)含量的检测方法.样品的制备使用液液萃取法,先将螺旋霉素溶于硫酸溶液,再用二氯甲烷萃取得到待测液.质谱检测使用多反应扫描模式,定量离子对为74.0→4.0,定性离子对为74.0→42.0.在0.25～50 μg/L范围内的ND...     

高效液相法测定螺旋霉素发酵液中的有机酸

 采用高效液相法在Zorbax 30 0 SBC18柱 (5 μm ,4 6mmi.d .× 15cm)上以 0 0 1mol/L磷酸缓冲液(pH 2 32 )和甲醇的二元流动相梯度分离测定了螺旋霉素发酵液中的有机酸 ,流动相的流速为 0 6mL/min ,紫外检测波长为 2 10nm。实验结果表明 ,该方法的相对标准偏差为 0 33%～ 0 10 % ,回收率为 99 95 %～ 10 0 0 8%。方法简便、快速、可靠。     

超高效液相色谱-串联质谱法同时测定制药废水中10种抗生素

建立了一种同时测定制药废水中3类10种抗生素的超高效液相色谱-串联质谱分析方法。水样用固相萃取柱富集净化,通过比较在不同的固相萃取柱和洗脱液等条件下水样中目标物的回收率,优化了前处理方法。采用Agilent C18色谱柱(75 mm×2.1 mm, 2.7 μm),以0.2%(v/v)甲酸水溶液和乙腈为梯度洗脱的流动相,在电喷雾-多反应监测模式下进行定性定量分析。实验结果表明:在0.1~1000 μg/L范围内,6种氨基糖苷类抗生素、螺旋霉素及3种氟喹诺酮类抗生素的峰面积与质量浓度的线性关系良好(r² > 0.995),方法检出限为0.07~4.37 ng/L,定量限为0.22~14.55 ng/L;目标抗生素的加标水平为0.002~40 μg/L时,平均回收率为50.4%~114.1%,相对标准偏差均不高于9.89%(n=3)。基于上述方法,对江苏省某制药厂废水中相关物质进行检测,在各废水处理单元中检出3种目标抗生素,质量浓度范围为0.46~1033.60 μg/L。该方法准确可靠、灵敏度高,适用于制药厂废水中氨基糖苷类抗生素、螺旋霉素和氟喹诺酮类抗生素的检测。     

高效液相色谱-串联质谱法同时测定水体和沉积物中12种有机磷酸酯类化合物

建立了高效液相色谱-质谱联用技术结合固相萃取和液液萃取方法检测水体和沉积物中12种磷酸酯类(OPEs)化合物残留的方法.水样样品经HLB固相萃取柱富集,乙酸乙酯洗脱两次,沉积物样品以乙腈超声萃取,旋转蒸发至干,用超纯水稀释后重复水样处理步骤,采用ZORBAX Eclipse Plus C18色谱柱(150 mm×2.1 mm, 3.5 μm)进行分离,以0.2%甲酸-甲醇作为流动相进行梯度洗脱,采用正离子MRM监测模式,外标法定量分析.水样中,12种OPEs在0.05、0.10和0.50 μg/L加标水平下,除TMP (28.5%~47.8%)和TEHP (22.4%~73.8%) 外,其余目标化合物的平均回收率为66.4%~115.0%,相对标准偏差为0.5%~9.1%,方法定量限(MOQ)为0.001~0.050 μg/L;沉积物中,在5、10和50 μg/kg加标水平下,除TMP(35.7%~44.9%)、TCEP (31.2%~48.9%)外,其余目标化合物的平均回收率为65.9%~120.0%,相对标准偏差为0.01%~9.5%,方法定量限(MOQ)为0.02~2.0 μg/kg(dw).基于上述方法对太湖水样和沉积物样品中目标化合物定量检测分析,∑OPEs含量分别为0.1~1.7 μg/L和8.1~420 μg/kg dw.     

一滴溶剂微萃取-毛细管气相色谱法分析水中的七种硝基苯类化合物

用一滴溶剂微萃取(SDME)-毛细管气相色谱联用技术测定水中的硝基苯、硝基甲苯类和硝基氯苯类化合物,对影响萃取的因素如萃取溶剂种类、液滴体积、搅拌速度、针尖入水深度、水样体积、萃取时间、萃取温度等进行了优化,结果表明:硝基苯和硝基甲苯类化合物在0.8～32 μg/L 范围内,硝基氯苯类化合物在0.04～3.2 μg/L 范围内均呈现良好的线性(r2>0.999),检出限可达0.01～0.3 μg/L。自来水加标样品测定的相对标准偏差和平均回收率(n=5)范围分别为3.1%～7.9%和101%～105%,废水加标样品测定的相对标准偏差和平均回收率(n=5)范围分别为3.3%～7.9%和92.5%～97.0%。优化后的SDME具有环保、灵敏、快速、简便等特点,适用于萃取水中的痕量硝基苯、硝基甲苯类和硝基氯苯类化合物。     

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%.     

ASE-HPLC检测某型号球形发射药中的叠氮硝胺、硝化甘油、Ⅱ号中定剂含量的研究

采用快速溶剂萃取(ASE)技术和高效液相色谱法测定某球形药中叠氮硝胺(DIANP)、硝化甘油(NG)和II号中定剂(C2)的含量.ASE提取条件:二氯甲烷做萃取溶剂,萃取温度100℃,静态萃取10 min,萃取2次.HPLC测定条件:YWG C18柱(150×4.6 mm,10μm),以甲醇和水作为流动相,梯度洗脱,流速1 mL/min,检测波长210nm.测定结果表明DIANP、NG、C2平均回收率分别为99.6%、100.3%、99.4%,RSD分别为0.7%、0.8%、0.9%(n=5),检出限分别为2.1、1.5和0.2 mg/L,线性范围分别为0.02~0.98 g/L,0.03~1.38 g/L,0.002~0.124g/L.用此方法共检测某批球形发射药样品5份,检测结果与滴析-HPLC法检测结果相当.     

液相色谱在线净化-电喷雾串联质谱测定水产品中大环内酯和林可胺类药物残留

建立了水产品中大环内酯类抗生素[红霉素(ERM)、罗红霉素(ROM)、替米卡星(TIL)、泰乐菌素(TYL)、北里霉素(KIT)、交沙霉素(JOS)、竹桃霉素(OLM)、螺旋霉素Ⅰ(SPM-Ⅰ)]和林可胺类(林可霉素(LIN)和氯林可霉素(CLD))的高效液相色谱-电喷雾串联质谱(LC-ESI-MS/MS)检测方法.样品经提取、反相液相色谱分离净化后进行质谱分析,在选择反应监测模式(SRM)下进行特征母-子离子对信号采集.根据保留时间和母离子及两个特征子离子信息定性分析,以基峰离子进行定量.大环内酯类残留的检出限(S/N=3)为0.1～0.2μg/kg,定量限为1.0μg/kg,在1.0～200 ng/mL时峰强度与质量浓度的线性关系良好(R~2 >0.99).在虾、鳗鱼和带鱼3种基质中1.0、2.0、10.0μg/kg 3个添加水平下,除个别药物外,药物的平均回收率范围为64%～114%,RSD<12%.该法适用于各种水产品中大环内酯类残留的分析.     

Determination of spiramycin and neospiramycin antibiotic residues in raw milk using LC/ESI‐MS/MS and solid‐phase extraction

A simple confirmatory method for the determination of spiramycin and its metabolite neospiramycin in raw milk using LC ESI MS/MS is presented. Macrolide residues in raw milk were extracted by ACN, and sample extracts were further cleaned up and concentrated using SPE cartridges. Both spiramycin and neospiramycin were protonated in electrospray positive ion mode to form singly and/or doubly charged pseudomolecular ions. Data acquisition was achieved using multiple reaction monitoring, i.e., two transitions, for quantification and confirmation. Matrix‐matched standard calibration curves were utilized to achieve the best accuracy for the method. The method performance was evaluated according to both a conventional validation procedure and a designed experimental result. The measurement uncertainty arising from accuracy and precision was estimated. The method accuracy, expressed as a percentage of an overall recovery, was from 82.1 to 108.8%, and its intermediate precision was less than 20%. LC/ESI‐MS/MS method LODs (S/N ? 3:1) of spiramycin and neospiramycin were less than 1.0 μg/kg.     

固相萃取/液相色谱-串联质谱法检测医院废水中21种抗生素药物残留

应用固相萃取及高效液相色谱-串联质谱技术,建立了医院废水中12种磺胺、4种喹诺酮、3种四环素以及罗红霉素和甲氧苄氨嘧啶等21种抗生素的定性定量方法。水样经HLB小柱萃取富集,使用10%甲醇溶液净化,经甲醇洗脱定容后,以高效液相色谱-串联质谱多反应监测离子模式(MRM)对目标物进行分析。在优化实验条件下,21种抗生素的线性范围为1.0～500μg/L,相关系数r2>0.99,方法检出限为0.005～0.022μg/L。在加标量为0.05μg/L和1.0μg/L时,空白加标回收率分别为71%～105%和76%～111%,RSD均小于15%。以医院废水为基质,21种抗生素的加标回收率为71%～135%,RSD小于25%。该方法简捷、快速、准确,能够实现医院废水中多种抗生素药物残留的同时分析。     

Determination of 38 antibiotics in raw and treated wastewater from swine farms using liquid chromatography-mass spectrometry

The present study firstly aimed at developing a multi-residue method to identify and quantify 38 veterinary antibiotics (belonging to five different classes) not only for raw swine wastewater but also for wastewater differently treated by different units. The proposed method is based on a solid-phase extraction procedure and ultra high performance liquid chromatography with mass spectrometry. For sample preparation, the optimal loading sample volume was selected as 50 mL, the pH of which was adjusted to approximately 3.0 using formic acid. Then 0.1 g/L ethylenediaminetetraacetic acid disodium salt was added. The recovery rates for different types of wastewaters were in the range of 35.94–124.51% and the relative standard deviations were in the range of 0.36–14.62%. All the matrix standard curves exhibited high linearity (0.9956–0.9999). The matrix effects for the target antibiotics ranged from –61.73 to +148.75%. To ensure the practicality of the method, we performed the detection of the actually added concentration to determine method detection limits and quantitation limits. The quantitation limits of most of the target antibiotics were 0.04 μg/L, except for spiramycin (0.1 μg/L) and roxithromycin (0.2 μg/L). This optimized and validated method was applied to analyze antibiotic residues in swine water samples from four swine farms.     

蜂王浆产品中5种大环内酯类抗生素残留量的高效液相色谱-质谱/质谱检测方法

建立了高效液相色谱-质谱/质谱测定蜂王浆中5种大环内酯类抗生素(螺旋霉素、竹桃霉素、泰乐菌素、罗红霉素、交沙霉素)残留的方法。先用三氯乙酸沉淀蜂王浆中的蛋白质,上层清液再用乙腈提取、C18小柱净化。每种抗生素选择一个母离子和两个子离子进行监测。5种大环内酯类抗生素在0.002～0.05 mg/L 范围内与其峰面积具有良好的线性关系,检测低限均为20 μg/kg,3个加标水平（每种抗生素的添加水平均为20, 100 和 200 μg/kg）下的加标回收率为73.0%～90.2%,相对标准偏差为5.6%～10.5%。     

UPLC-MS/MS法对动物源性食品中12种大环内酯类抗生素残留的测定

建立了超高效液相色谱-串联质谱(UPLC-MS/MS)法测定动物源性食品中12种大环内酯类抗生素(林可霉素、阿奇霉素、螺旋霉素、替米考星、竹桃霉素、红霉素、泰乐霉素、吉他霉素、罗红霉素、克拉霉素、麦迪霉素、交沙霉素)的方法.样品均质后,用乙腈提取,正己烷净化,无水硫酸钠脱水.乙腈提取液减压浓缩后,氮气流吹干,甲醇溶解定容;采用UPLC-MS/MS电喷雾多反应监测模式检测,基质匹配标准曲线定量.实验结果表明,12种大环内酯化合物在5 ～100 μg/kg范围内线性关系良好,检出限均为5.0 μg/kg,定量下限为10 μg/kg.5种空白基质样品中,10、25、50 μg/kg加标水平的平均回收率为60% ～117%,相对标准偏差均在20%以内.该方法灵敏度高、重复性好,各项技术指标均满足国内外相关法规要求,可用于动物源性食品中12种大环内酯类抗生素残留的检测.     

Multiresidue chromatographic method for the determination of macrolide residues in muscle by high-performance liquid chromatography with UV detection.

A high-performance liquid chromatographic (HPLC) method for the simultaneous determination of tilmicosin, tylosin, spiramycin, and its major metabolite neospiramycin was developed that is suitable for porcine, bovine, and poultry muscles. Macrolide residues were extracted from muscle with acetonitrile, fat was removed by liquid-liquid extraction with isooctane, and the extract was then cleaned on Bond Elut C18 cartridges. The HPLC separation was performed on an Inertsil ODS3 C18 column (150 x 4 mm) with 0.05% trifluoroacetic acid-acetonitrile in a gradient mode. Two different chromatographic gradients were used for tilmicosin-tylosin and spiramycin-neospiramycin, and the detection wavelengths were 287 and 232 nm, respectively. The method was validated from 1/2 the maximum residue limit (MRL) to 4 times the MRL with pork muscle samples. Mean recoveries were 60, 63.5, 51, and 42% for tilmicosin, tylosin, spiramycin, and neospiramycin, respectively. The detection limits are 15 micrograms/kg for tilmicosin and tylosin, 30 micrograms/kg for spiramycin, and 25 micrograms/kg for neospiramycin. Linearity, precision, and accuracy of the method were also tested.     

A quantitative method for residues of macrolide antibiotics in porcine kidney by liquid chromatography/tandem mass spectrometry

An LC/MS/MS-based multiresidue quantitative method was developed for the macrolides erythromycin A, neospiramycin I, oleandomycin, spiramycin I, tilmicosin, and tylosin A in porcine kidney tissues. The Canadian Food Inspection Agency (CFIA) had as part of its analytical scope an LC/UV method for quantification of residues of two macrolide antibiotics, tilmicosin and tylosin A, in the kidney, liver, and muscle of cattle, swine, and poultry. The method could not reliably detect concentrations below 10 microg/kg. To increase the scope of the CFIA's analytical capabilities, a sensitive multiresidue quantitative method for macrolide residues in food animal tissues was required. Porcine kidney samples were extracted with acetonitrile and alkaline buffer and cleaned-up using silica-based C18 SPE cartridges. Sample extracts were analyzed using LC/MS/MS with positive electrospray ionization. Fitness for purpose was verified in a single-laboratory validation study using a second analyst. The working analytical range was 5 to 50 microg/kg. LOD and LOQ were 0.5 to 0.6 microg/kg and 1.5 to 3.0 microg/kg, respectively. Limits of identification were 0.5 to 2.0 microg/kg. Relative intermediate precisions were 8 to 17%. Average absolute recoveries were 68 to 76%.     

Determination of organic pollutants in coking wastewater by dispersive liquid–liquid microextraction/GC/MS

A method based on dispersive liquid–liquid microextraction coupled with GC/MS was developed for quantitative analysis of the major organic pollutants listed in the United States Environmental Protection Agency method 8270 and the 15 European‐priority polycyclic aromatic hydrocarbons in coking wastewater. The major parameters such as extraction solvent, dispersive solvent, solution pH, and extraction time were systematically optimized. The optimum extraction conditions were found to be: 15 μL mixture of 2:1 v/v carbon tetrachloride and chlorobenzene as the extraction solvent, 0.75 mL ACN as the dispersive solvent, solution pH of 8, and extraction time of 2 min. For the major pollutants listed in the United States Environmental Protection Agency 8270, the linear ranges were 0.1 to 100 mg/L, the enrichment factors ranged from 452 to 685, and the relative recoveries ranged from 67.5 to 103.5% with RSDs of 4.0–9.1% (n = 5) at the concentrations of 10 mg/L under the optimum extraction conditions. For the 15 polycyclic aromatic hydrocarbons, the linear ranges were 0.1 to 100 μg/L, the enrichment factors ranged from 645 to 723, and the relative recoveries ranged from 94.5 to 107.6% with RSDs of 4.6–9.0% (n = 5) at the concentrations of 10 μg/L. The usefulness of the developed method was demonstrated by applying it in the analysis of real‐world coking wastewater samples.