凝胶渗透色谱结合气相色谱-负化学源质谱法分析鱼肉及鱼油中的多溴联苯醚和得克隆阻燃剂

建立了凝胶渗透色谱(GPC)结合气相色谱-负化学源质谱(GC-NCI/MS)检测鱼肉及鱼油中8种多溴联苯醚(PBDEs)同系物及2种得克隆阻燃剂(DP)的分析方法。试样中加入内标物BDE-77和13C12-BDE-209后进行索氏提取,提取液经自动GPC系统除脂,多层硅胶层析柱净化后,在15 m长的毛细管气相色谱柱上分离,NCI/MS以选择离子监测方式检测目标化合物。以鱼肉样品为基质,当PBDEs的加标水平为0.2 ng/g和2 ng/g、BDE-209和DP的加标水平相应提高10倍时,其平均加标回收率为71.1%～121.4%,相对标准偏差为2.96%～13.31%(n=5);以信噪比(S/N)为3计算方法的检出限(LOD)为2.2～39.8 ng/kg。用该方法检测市售鱼肉及鱼油样品,其中多溴联苯醚总含量为2.18～15.93 ng/g,以BDE-209、BDE-47为主,两种DP均未检出。该方法准确、灵敏度高,能够满足富含脂质的动物性样品中痕量DP和PBDEs残留的分析要求。     

凝胶渗透色谱结合气相色谱-负化学源质谱法分析鱼肉及鱼油中的多溴联苯醚和得克隆阻燃剂

建立了凝胶渗透色谱(GPC)结合气相色谱-负化学源质谱(GC-NCI/MS)检测鱼肉及鱼油中8种多溴联苯醚(PBDEs)同系物及2种得克隆阻燃剂(DP)的分析方法。试样中加入内标物BDE-77和13C12-BDE-209后进行索氏提取,提取液经自动GPC系统除脂,多层硅胶层析柱净化后,在15 m长的毛细管气相色谱柱上分离,NCI/MS以选择离子监测方式检测目标化合物。以鱼肉样品为基质,当PBDEs的加标水平为0.2 ng/g和2 ng/g、BDE-209和DP的加标水平相应提高10倍时,其平均加标回收率为71.1%～121.4%,相对标准偏差为2.96%～13.31%(n=5);以信噪比(S/N)为3计算方法的检出限(LOD)为2.2～39.8 ng/kg。用该方法检测市售鱼肉及鱼油样品,其中多溴联苯醚总含量为2.18～15.93 ng/g,以BDE-209、BDE-47为主,两种DP均未检出。该方法准确、灵敏度高,能够满足富含脂质的动物性样品中痕量DP和PBDEs残留的分析要求。     

超声辅助萃取-气相色谱-负化学电离源质谱法测定室内灰尘样品中8种常见多溴联苯醚

建立了室内灰尘样品中8种常见多溴联苯醚(PBDEs: BDE-28、BDE-47、BDE-99、BDE-100、BDE-153、BDE-154、BDE-183和BDE-209)的气相色谱-负化学电离源质谱(GC-NCI/MS)分析方法。样品经吸尘器采集、正己烷超声萃取、浓缩后,采用GC-NCI/MS测定。结果表明,方法的加标回收率为53.2%～107.6%,日内测定的相对标准偏差(RSD)为2.8%～16.5%,日间测定的RSD为6.4%～22.6%。除了BDE-209的检出限(信噪比为3)为0.15 ng/g外,其他多溴联苯醚的检出限为0.003～0.015 ng/g。该方法灵敏度高,准确度和精密度好,简便快速,溶剂消耗量少,适用于灰尘中三溴～十溴联苯醚的测定。     

固相萃取-浓硫酸净化-气相色谱/三重四极杆串联质谱法测定水中的8种多溴联苯醚

建立了固相萃取-浓硫酸净化-气相色谱/三重四极杆串联质谱(SPE-GC-MS/MS)分析水中8种多溴联苯醚(PBDEs,BDE-28,BDE-47,BDE-99,BDE 100,BDE-153,BDE-154,BDE-183和BDE-209)的方法。方法采用改进的色谱柱可同时分析高溴代联苯醚BDE209,采用浓硫酸净化固相萃取后的样品和串联质谱特有的多反应监测模式,可以很好地去除基质干扰和提高定性的准确性。通过优化三重四极杆串联质谱的碰撞电压、扫描峰宽和离子对等条件,使8种多溴联苯醚的检测灵敏度显著提高。8种多溴联苯醚的浓度在0.1～50 ng/mL(BDE209:1～500 ng/mL)范围内线性良好,回归系数均大于0.9997。方法回收率在49%～110%,相对标准偏差在1.4%～6.0%之间。方法可用于实际地表水体中PBDEs的定量检测。     

动物肝脏中九种多溴联苯醚残留量的GC—NCI／MS分析

建立了动物肝脏中9种PBDEs残留量的气相色谱-负化学离子源/质谱(GC-NCI/MS)的分析方法。动物肝脏样品经V(正己烷)∶V(丙酮)=1∶1超声辅助提取,中性与酸性硅胶层析柱净化和V(正已烷)∶V(CH2Cl2)=1∶1洗脱和浓缩后,以PCB-103为内标物,采用GC-NCI/MS的选择离子监测方式(SIM)对其中的9种PBDEs残留量进行了定性与定量分析。当动物肝脏空白样品的加标质量浓度为5.0、20.0μg/kg(PBDE-183为6.0、24.0μg/kg)时,9种PBDEs的平均加标回收率为75.1%~88.2%,相对标准偏差为3.3%~7.9%,方法检出限均小于0.07μg/kg;线性范围除PBDE-183为0.12~600.0μg/kg外,其余8种PBDEs为0.1~500.0μg/kg,相关系数都大于0.9993。所建立的分析方法已用于5种动物肝脏的8个样品中9种PBDEs残留量的分析。     

固相萃取结合超高效液相色谱-串联质谱法及气相色谱-负化学源质谱法测定人血清中的四溴双酚A、六溴环十二烷和多溴联苯醚

建立了固相萃取同时提取、净化血清中四溴双酚A(TBBPA)、α, β, γ-六溴环十二烷(HBCD)和8种多溴联苯醚(PBDEs)同系物的样本前处理方法,并结合色谱-质谱分离分析技术检测人血清样本中该类化合物的含量。试样在加入各自的同位素内标物后以甲基叔丁基醚/正己烷(1:1, v/v)混合溶剂进行萃取,再经浓硫酸去除脂肪后,以LC-Si固相萃取柱分离HBCD/TBBPA和PBDEs。采用分步检测的方式,在50 mm长BEH C18反相色谱柱上以超高效液相色谱-串联质谱(UPLC-MS/MS)的多反应监测模式(MRM)检测HBCD和TBBPA,在15 m长的毛细管柱上以气相色谱-负化学源质谱(GC-NCI/MS)的选择离子监测模式(SIM)检测PBDEs。以胎牛血清为空白基质,当HBCD、TBBPA和BDE-209的加标水平为0.5 ng/g和5 ng/g、三溴至七溴联苯醚的加标水平为0.05 ng/g和0.5 ng/g时,它们的平均加标回收率为80.3%～108.8%,相对标准偏差为1.02%～11.42%(n=5);以信噪比(S/N)为3计算,方法的检出限(LOD)为1.81～42.16 pg/g。采用该方法对实际样品进行测定,结果表明,本方法快速、准确、灵敏度高,能够满足血清中HBCD、TBBPA和PBDEs残留的同时提取及测定的要求。     

海产品中九种多溴联苯醚残留的气相色谱-负化学离子源／质谱法分析

建立了海产品中九种多溴联苯醚(PBDEs)残留的气相色谱-负化学离子源/质谱(GC-NCI/MS)分析方法.采用正己烷提取剂超声提取、Florisil硅藻土净化柱净化和正己烷洗脱剂洗脱的样品前处理方法,以PCB-103作为内标物,以GC-NCI/MS的选择离子监测方式(S1M)对海产品中九种PBDEs残留进行了定性与定量分析.分析方法的线性相关系数均≥0.9988,九种PBDEs两种添加浓度水平时的平均加标回收率为88.1%～97.3%,相对标准偏差为2.0%～6.6%,方法检出限均小于0.106 ng/g.线性范围除PBDE-183为0.60～300.0 ng/g外,其余八种PBDEs为0.50～250.0 ng/g.同时分析了紫菜、海带、鲜海带、鱼干和花蛤干等海产品,在这些海产品干货中都检出了较多种的PBDEs残留.     

蔬菜中26种农药残留的高效液相色谱-串联质谱法测定

建立了蔬菜中26种农药的反相高效液相色谱-电喷雾串联质谱 (LC-ESI MS/MS) 检测方法.蔬菜样品经含0.1%醋酸的乙腈提取、浓缩、分散型固相萃取净化,液相色谱串联质谱测定,内标法定量.26种农药在5.0 ～200 μg/L范围内线性关系良好(r2＞0.997).在豌豆、菠菜、脱水葱3种基质中的检出限和定量下限均为2.0 μg/kg和5.0 μg/kg.在5.0、10.0、40.0 μg/kg 3个添加水平下,26种农药的回收率为70% ～110%,精密度(RSD)小于15%.方法准确、灵敏、简单,适用于蔬菜中26种农药残留的同时测定.     

高效液相-电喷雾串联质谱法测定动物肌肉组织中的糖皮质激素

本实验建立了肌肉组织中氢化可的松、可的松、泼尼松和地塞米松含量的高效液相色谱-电喷雾串联质谱(LC-ESI-MS/MS)检测方法.样品经酶水解、乙酸乙酯提取、HLB固相萃取净化,C8色谱柱分离,在多反应选择性监测模式(MRM)下采用负离子模式进行信号采集和测定.4种糖皮质激素的检出限为0.13 ～0.25 μg/kg,定量限为0.25 ～ 0.5 μg/kg.在0.5～50.0 μg/L范围内具有良好的线性关系(R2＞0.99).在0.5,5.0和10.0μg/kg基质加标水平下,4种物质的平均回收率为74.0％ ～ 101.8％,相对标准偏差0.7％ ～8.6％.     

气相色谱-串联质谱法同时测定食品中18种邻苯二甲酸酯

建立了凝胶色谱(GPC)净化、气相色谱-串联质谱(GC-MS/MS)多反应监测模式同时测定油脂食品中18种邻苯二甲酸酯的方法.优化了前处理和分析条件,样品加标浓度在2 mg/kg时的回收率在80％～120％之间,相对标准偏差均小于10％,检出限为5 μg/kg,定量限为20 μg/kg,在20～1 000 μg/mL范围内,具有良好的线性关系,能够满足大量样品快速准确分析的需要.     

Analysis of polybrominated diphenyl ethers (PBDEs) by liquid chromatography with negative-ion atmospheric pressure photoionization tandem mass spectrometry (LC/NI-APPI/MS/MS): application to house dust

Eight polybrominated diphenyl ether (PBDE) congeners of primary interest to the US EPA were separated using reverse-phase liquid chromatography on an octadecylsilane column. BDE-28, BDE-47, BDE-99, BDE-100, BDE-153, BDE-154, BDE-183, and BDE-209 were baseline-resolved under isocratic conditions in 92:8 methanol/water (v/v). Negative-ion atmospheric pressure photoionization (NI-APPI) with a toluene dopant produced precursor ions corresponding to [M–Br+O]^– for the eight congeners studied. Each congener was quantified by tandem mass spectrometry through a unique multiple reaction monitoring (MRM) transition. On-column limits of detection were between 2.4 and 27.8 pg for the eight congeners studied, with an intra-day method precision of 9%. The LC/NI-APPI/MS/MS method was validated for the analysis of the eight PBDE congeners in NIST SRM 2585 (Organics in House Dust). Pressurized liquid extraction (PLE) with subsequent LC/NI-APPI/MS/MS analysis afforded quantitative recovery for all eight PBDE congeners with recoveries ranging from 92.7 to 113%. The liquid-phase separation of the LC/NI-APPI/MS/MS method is not prone to the thermal degradation issues that plague splitless GC based analyses of highly brominated PBDEs such as BDE-209.     

Supercritical fluid extraction of polybrominated diphenyl ethers (PBDEs) from house dust with supercritical 1,1,1,2-tetrafluoroethane (R134a)

The extraction of polybrominated diphenyl ethers (PBDEs) from SRM 2585 (Organic Contaminants in House Dust) was investigated using supercritical fluid R134a as an extraction solvent. Three methods of dust extraction were studied: (1) extraction of dry dust, (2) extraction of dry dust dispersed on Ottawa sand and (3) extraction of dust wet with dichloromethane. For each of the three sample preparation methods, extracts at three temperatures (110, 150, and 200 °C) above the critical temperature of R134a were performed. Eight PBDE congeners (BDE-28, -47, -99, 100, -153, -154, -183, and -209) in the SFE extracts were analyzed by liquid chromatography negative-ion atmospheric pressure photoionization tandem mass spectrometry (LC/NI-APPI/MS/MS). The optimum extraction of PBDEs from house dust using supercritical R134a is obtained when the dust is pre-wet with dichloromethane prior to extraction to swell the dust. For all sample preparation methods, higher temperatures afforded higher percent recoveries of the eight PBDE congeners. Only a combination of high-temperature (200 °C) and pre-wetting the dust with dichloromethane produced high recovery of the environmentally important, fully brominated PBDE congener, BDE-209.     

New perspective on the determination of flame retardants in sewage sludge by using ultrahigh pressure liquid chromatography–tandem mass spectrometry with different ion sources

Analysis of 11 polybrominated diphenyl ethers (PBDEs), tetrabromobisphenol A bis 2,3-dibromopropylether (TBBPA-bis), tetrachlorobisphenol A (TCBPA), tetrabromobisphenol A (TBBPA) and hexabromocyclododecanes (HBCDs) was optimized by ultrahigh pressure liquid chromatography/tandem mass spectrometry (UPLC–MS/MS) operating in negative ion (NI) mode. Electrospray ionization (ESI), atmospheric pressure photoionization (APPI) and atmospheric pressure chemical ionization (APCI) sources were tested and for PBDEs APCI gave higher sensitivity than APPI while for TBBPA-bis APCI and APPI showed similar performance. ESI was the best option for TCBPA, TBBPA and HBCDs. Detection limits were between 20 and 59 fg for the compounds analyzed by ESI, 0.10 and 0.72 pg for PBDEs and 6 pg for TBBPA-bis. The matrix effect of sewage sludge extract was also tested showing negligible ion suppression for APCI and an increase of the background level of all investigated pollutants leading to a worsening of the limits of quantification by a factor between 1.2 and 3.3. The UPLC-APCI/MS/MS method for PBDEs, after pressurized liquid extraction (PLE), was validated by comparison with the concentration values from the NIST 1944 standard reference material. The advantages of the methods include low detection limits, PBDE congeners specificity using selected multiple reaction monitoring (MRM) transitions, and the absence of thermal degradation of higher PBDE congeners, especially BDE-209. The methods were applied for the determination of the above reported flame retardants in sewage sludge in order to get more information about the degradation on PBDEs (in particular BDE-209) during municipal wastewater treatments.     

Simple approach based on ultrasound-assisted emulsification-microextraction for determination of polibrominated flame retardants in water samples by gas chromatography–mass spectrometry

A simple, efficient, innovative and environmentally friendly analytical technique was successfully applied for the first time for the extraction and preconcentration of polybrominated diphenyl ethers (PBDEs) from water samples. The PBDEs selected for this work were those most commonly found in the literature in natural water samples: 2,2′,4,4′-tetraBDE (BDE-47), 2,2′,4,4,5-pentaBDE (BDE-99), 2,2′,4,4,6-pentaBDE (BDE-100) and 2,2,4,4′,5,5′-hexaBDE (BDE-153). The extracted PBDEs were separated and determined by gas chromatography–mass spectrometry (GC–MS). The extraction/preconcentration technique is based on ultrasound-assisted emulsification-microextraction (USAEME) of a water-immiscible solvent in an aqueous medium. Several variables including, solvent type, extraction time, extraction temperature and matrix modifiers were studied and optimized over the relative response the target analytes. Chloroform was used as extraction solvent in the USAEME technique. Under optimum conditions, the target analytes were quantitatively extracted achieving enrichment factors (EF) higher than 319. The detection limits (LODs) of the analytes for the preconcentration of 10 mL sample volume were within the range 1–2 pg mL⁻¹. The relative standard deviations (RSD) for five replicates at 10 pg mL⁻¹ concentration level were <10.3%. The calibration graphs were linear within the concentration range of 5–5000 pg mL⁻¹ for BDE-47 and BDE-100; and 5–10,000 pg mL⁻¹ for BDE-99 and BDE-153, respectively. The coefficients of estimation were ≥0.9985. Validation of the methodology was performed by standard addition method at two concentration levels (10 and 50 pg mL⁻¹). Recovery values were ≥96%, which showed a successful robustness of the analytical methodology for determination of picogram per milliliter of PBDEs in water samples. Significant quantities of PBDEs were not found in the analyzed samples.     

固相萃取-气相色谱-负化学源质谱法测定人血清中的多溴联苯醚

采用OasisHLB固相萃取柱萃取血清中的多溴联苯醚(PBDEs),经浓硫酸柱上除脂后,利用气相色谱-负化学源质谱法测定BDE-17、28、47、66、99、100、153、154、183和209共10种PBDEs组分。BDE-209的测定采用DB-5 ms色谱柱(15 m×0.25 mm×0.1 μm),其他组分采用VF-5 ms色谱柱(30 m×0.25 mm×0.25 μm)。对样品中蛋白质的去除溶剂和固相萃取条件(如洗脱溶剂及其用量)进行了优化。胎牛血清中的加标回收试验结果显示,各PBDEs单体相对于内标的平均回收率为78.5%～109.7%,日内测定的相对标准偏差(RSD)为0.3%～7.4%,日间测定的RSD为1.4%～14.1%。胎牛血清中三溴～七溴联苯醚的检出限(信噪比为3)为0.10～0.27 ng/L;定量限(信噪比为10)除了BDE-209为7.91 ng/L外,其他PBDEs为0.35～0.91 ng/L。采用本方法测定标准参考物质SRM1957和SRM1958,结果在参考值范围内。实验结果表明,本方法灵敏度高、准确度和精密度好,简便快速,溶剂消耗量少,适用于人体血清中三至十位溴取代联苯醚的测定。     

Determination of polybrominated diphenyl ethers in freshwater fishes from a river polluted by e-wastes

Analytical method using mass spectrometric techniques was applied for the determination of polybrominated diphenyl ethers (PBDEs) in freshwater fishes. Fish samples collected from Nanyang River contaminated by the recycling electron-wastes (e-wastes) materials were prepared by using Soxhlet extraction and multiple-step column chromatographic clean-up. PBDEs were determined by gas chromatography (GC) coupled with ion trap mass spectrometry (for mono- to hepta-BDEs) and quadrupole mass spectrometry (for BDE-209). The method performance was evaluated with the recovery of ¹³C-labeled internal standards and with the analysis of certified reference biota. The obtained recoveries ranged from 75 to 125% with a relative standard deviation of lower than 10% for 16 PBDE congeners. The total PBDE (ΣPBDE) concentrations in fishes showed the following trend: grass carp < mud carp < crucian carp < silver carp < carp. ΣPBDE concentrations in the abdomen, back and tail muscles of carp ranged from 766, 458 and 530 ng/g w.w., and 53, 52, 45 ng/g w.w. in grass carp, respectively. The ΣPBDE concentrations in abdomen muscles were no significantly higher than in back and tail muscles in carp, crucian carp, grass carp and mud carp. PBDE congener concentrations in muscles correlated well with their lipid content. BDE-47 and BDE-28 were the most abundant congeners followed by BDE-17, BDE-15, BDE-66, BDE-154 and BDE-153 in fishes collected from Guiyu.