多壁碳纳米管固相萃取-高效液相色谱-串联质谱法测定食品接触材料中双酚-二环氧甘油醚的迁移量

建立了测定食品接触材料中6种双酚-二环氧甘油醚(双酚A二缩水甘油醚(BADGE)及其衍生物双酚A(2,3-二羟丙基)甘油醚(BADGE•H2O)、双酚A(3-氯-2-羟丙基)甘油醚(BADGE•HCl)、双酚A(3-氯-2-羟丙基)(2,3-二羟丙基)醚(BADGE•H2O•HCl)和双酚F二缩水甘油醚(BFDGE)及其衍生物双酚F双(3-氯-2-羟丙基)甘油醚(BFDGE•2HCl))迁移到食品中的迁移量的高效液相色谱-串联质谱法(HPLC-MS/MS)。样品以叔丁基甲醚(MTBE)为提取溶剂,超声提取,提取液经多壁碳纳米管(MWCNTs)固相萃取(SPE)柱富集、净化。以COSMOSIL C18为分析柱,流动相为0.1%甲酸的5 mmol/L醋酸铵溶液和甲醇。6种双酚-二环氧甘油醚在1.0～100 μg/L范围内线性关系良好(r2＞0.9991)。在3个添加水平下,6种目标化合物的回收率范围为78.6%～89.9%,相对标准偏差小于10%。方法检出限范围为0.5～1.5 μg/L。该方法操作简单,灵敏度高,可应用于食品接触材料中双酚-二环氧甘油醚迁移量的快速检测。     

食品罐内壁涂料中双酚-二缩水甘油醚的快速检测和迁移规律

建立了快速、简便的超高效液相色谱法同时测定食品模拟物中双酚A-二缩水甘油醚(BADGE)、双酚F-二缩水甘油醚(BFDGE)及其衍生物特定迁移量的方法。采用水、3%乙酸、10%乙醇和葵花籽油4种食品模拟物在60℃、10 d的条件下模拟了食品罐内壁涂料中双酚-二缩水甘油醚的迁移。水性食品模拟物直接进样,葵花籽油模拟物采用乙腈提取,提取液经固相萃取净化后进样。迁移到水性食品模拟物中的BADGE、双酚A-(3-氯-2-羟丙基)甘油醚(BADGE·HCl)发生水解,分别转化成双酚A-二(2,3-二羟丙基)醚(BADGE·2H2O)和双酚A-(3-氯-2-羟丙基)(2,3-二羟丙基)醚(BADGE·H2O·HCl);迁移到油性模拟物中的BADGE和BADGE·HCl则没有发生水解。9种双酚-二缩水甘油醚在0.05~10 mg/L范围内线性关系良好,水性食品模拟物和油性食品模拟物中方法的检出限分别为5μg/L和20μg/kg。应用本方法对10种未接触过食品的空罐进行了检测,有5种样品中检出了BADGE及其衍生物,其中1种样品中BADGE·2H2O(或BADGE)和BADGE·H2O·HCl(或BADGE·HCl)在4种食品模拟物中的迁移量均超过了欧盟EC/1895/2005规定的限量。     

固相萃取-高效液相色谱-串联质谱测定水中8种双酚-二环氧甘油醚

建立了水中8种双酚-二环氧甘油醚（双酚A二缩水甘油醚（BADGE）及其衍生物双酚A（3-氯-2-羟丙基）甘油醚（BADGE·5HCl）、双酚A双（3-氯-2-羟丙基）醚（BADGE·52HCl）、双酚A（2,3-二羟丙基）甘油醚（BADGE·5H₂O）、双酚A双（2,3-二羟丙基）醚（BADGE·52H₂O）、双酚A（3-氯-2-羟丙基）（2,3-二羟丙基）醚（BADGE·5HCl·5H₂O）和双酚F-二环氧甘油醚（BFDGE）及其衍生物双酚F双（3-氯-2-羟丙基）醚（BFDGE·52HCl））的固相萃取-高效液相色谱-串联质谱（SPE-HPLC-MS/MS）测定方法。10个饮用水接触涂料样品在室温避光条件下,以超纯水浸泡（24±1）h,然后取200 mL经C₁₈固相萃取柱进行净化浓缩,以C₁₈色谱柱进行分离,以5 mmol/L醋酸铵、甲醇和水为流动相进行梯度洗脱,质谱多反应监测（MRM）模式检测,外标法定量。结果表明,8种双酚-二环氧甘油醚在0.007~5.00 μg/L线性关系良好,相关系数均大于0.9990,该方法对8种双酚-二环氧甘油醚的定量限为7~91 ng/L,回收率为79.1%~101%,RSD为4.0%~12%。该方法具有灵敏度高、选择性强的特点,能够满足水中双酚-二环氧甘油醚的快速检测和准确定量。     

罐装饮料中双酚A-二缩水甘油醚与双酚F-二缩水甘油醚及其衍生物的快速检测

建立了固相萃取/超高效液相色谱法测定罐装饮料中9种双酚-二缩水甘油醚,包括双酚A-二缩水甘油醚(BADGE)及其衍生物BADGE·2H2O、BADGE·H2O、BADGE·2HCl、BADGE·HCl、BADGE·H2O·HCl和双酚F-二缩水甘油醚(BFDGE)及其衍生物BFDGE·2H2O、BFDGE·H2O的快速检测方法。采用叔丁基甲醚为提取溶剂,涡旋振荡提取,提取液氮吹至近干后用甲醇-水(2∶3)溶解,采用PLS亲水亲酯柱固相萃取净化。以Shim-pack XR-ODS-Ⅲ为分析柱,乙腈-水为流动相进行梯度洗脱。9种双酚-二缩水甘油醚在0.05~10 mg/L范围内线性关系良好,回收率为83.8%~98.7%,RSD为2.3%~5.6%,方法检出限为20μg/kg。该方法操作简单、灵敏度高,可在10 min内对罐装饮料中9种双酚-二缩水甘油醚进行快速检测。     

鱼肉类罐头中双酚-二环氧甘油醚的固相萃取/HPLC-MS/MS法检测

建立了鱼肉类罐头中内分泌干扰物质双酚A二缩水甘油醚(BADGE)及其衍生物BADGE·H2O、BADGE·2H2O、BADGE·2HCl、BADGE·HCl·H2O和双酚F二缩水甘油醚(BFDGE)及其衍生物BFDGE·2H2O、BFDGE·2HCl 8种双酚-二环氧甘油醚的固相萃取/液相色谱-电喷雾串联质谱分析方法.以叔丁基甲醚为提取溶剂,采用超声波辅助溶剂萃取法萃取,萃取液用Waters Oasis HLB固相萃取柱进行净化浓缩.以Thermo Hypersil Gold C18色谱柱为分离柱,在正离子模式下以电喷雾电离串联质谱仪进行测定.考察了流动相组分和流动相添加剂对质谱离子化效率的影响,8种双酚-二环氧甘油醚在1.0 ～100.0 μg/L范围内线性关系良好(r≥0.99).在2.0、10.0和50.0 μg/kg的添加水平下,8种目标化合物的回收率为83% ～99%,相对标准偏差小于9.0%,方法的检出限为0.13 ～0.30 μg/kg.方法具有较高的灵敏度和准确度,能够满足鱼肉类罐头食品中双酚-二环氧甘油醚残留量的快速检测.     

5-(N-2-羟乙基)羟乙酰氨基-N,N′-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺的合成

5-氨基-N,N′-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(2)在N,N-二甲基乙酰胺中可直接与乙酰氧基乙酰氯反应,产物再经碱性水解得5-羟乙酰氨基-N,N′-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(3),后者再与氯乙醇反应生成5-(N-2-羟乙基)羟乙酰胺基-N,N′-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(1),经乙二醇甲醚/正丁醇重结晶,纯度高于99%(HPLC),反应总收率由39.3%(文献值)提高到55.1%.     

5-(N-2-羟乙基)羟乙酰氨基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺的合成

5-氨基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(2)在N,N-二甲基乙酰胺中可直接与乙酰氧基乙酰氯反应,产物再经碱性水解得5-羟乙酰氨基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(3),后者再与氯乙醇反应生成5-(N-2-羟乙基)羟乙酰胺基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(1),经乙二醇甲醚/正丁醇重结晶,纯度高于99%(HPLC),反应总收率由39.3%(文献值)提高到55.1%.     

系列缩水甘油醚类β-环糊精衍生物的合成及结构表征

以苯基缩水甘油醚、邻甲基酚缩水甘油醚及苯甲基缩水甘油醚(1～3)和β-环糊精为原料, 分别在弱碱水溶液(1.5%)和强碱水溶液(30%)中制备出系列缩水甘油醚类β-环糊精衍生物, 所得产物用自制硅胶色谱柱分离, 以V(正丙醇)∶V(水)∶V(浓氨水)＝6∶3∶1作为硅胶色谱柱分离纯化的洗脱剂, 得到单2位取代的苯氧基(或邻甲基苯氧基或苯甲氧基-2-羟丙基-β-环糊精(1a～3a)和单6位取代的苯氧基(或邻甲基苯氧基)-2-羟丙基-β-环糊精(1b～2b). 所得产品用薄层色谱、红外光谱、质谱和核磁共振波谱等手段进行了表征.     

5-(N-2-羟乙基)羟乙酰氨基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺的合成

5-氨基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(2)在N,N-二甲基乙酰胺中可直接与乙酰氧基乙酰氯反应, 产物再经碱性水解得5-羟乙酰氨基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(3), 后者再与氯乙醇反应生成5-(N-2-羟乙基)羟乙酰胺基-N,N'-双(2,3-二羟丙基)-2,4,6-三碘-1,3-苯二甲酰胺(1), 经乙二醇甲醚/正丁醇重结晶, 纯度高于99% (HPLC), 反应总收率由39.3% (文献值)提高到55.1%.     

聚(β-氯乙基缩水甘油醚)的合成及其酯化反应动力学

本文合成了β-氯乙基缩水甘油醚及其聚合物。结果表明, AlEt3-0.5H2O体系是β-氯乙基缩水甘油醚的一种有效的聚合引发剂。研究了聚(β-氯乙基缩水甘油醚)的酯化反应动力学, 并通过^1H NMR和IR光谱确立了酯化度的计算关系式。最后, 通过光交联的动力学研究发现, 酯化聚合物中的肉桂酰基含量为85%时, 材料的感光灵敏度最高。     

Fast liquid chromatography-tandem mass spectrometry for the analysis of bisphenol A-diglycidyl ether, bisphenol F-diglycidyl ether and their derivatives in canned food and beverages

In this work a fast liquid chromatography coupled with tandem mass spectrometry (LC–MS/MS) method using a C18 Fused Core™ column, was developed for the simultaneous analysis of bisphenol A diglycidyl ether (BADGE), bisphenol A (2,3-dihydroxypropyl) glycidyl ether (BADGE·H₂O), bisphenol A bis(2,3-dihydroxypropyl) ether (BADGE·2H₂O), bisphenol A (3-chloro-2-hydroxypropyl) glycidyl ether (BADGE·HCl), bisphenol A bis(3-chloro-2-hydroxypropyl) ether (BADGE·2HCl) and bisphenol A (3-chloro-2-hydroxypropyl)(2,3-dihydroxypropyl ether) (BADGE·HCl·H₂O) and bisphenol F diglycidyl ether (BFDGE), bisphenol F bis(2,3-dihydroxypropyl) ether (BFDGE·2H₂O), bisphenol F bis(3-chloro-2-hydroxypropyl) ether (BFDGE·2HCl). The LC method was coupled with a triple quadrupole mass spectrometer, using an ESI source in positive mode and using the [M+NH₄]⁺ adduct as precursor ion for tandem mass spectrometry experiments. The method developed was applied to the determination of these compounds in canned soft drinks and canned food. OASIS HLB solid phase extraction (SPE) cartridges were used for the analysis of soft drinks, while solid canned food was extracted with ethyl acetate. Method limits of quantitation ranged from 0.13 μg L⁻¹ to 1.6 μg L⁻¹ in soft drinks and 1.0 μg kg⁻¹ to 4.0 μg kg⁻¹ in food samples. BADGE·2H₂O was detected in all the analyzed samples, while other BADGEs such as BADGE·H₂O, BADGE·HCl·H₂O, BADGE·HCl and BADGE·2HCl were also detected in canned foods.     

Simultaneous determination of NOGE-related and BADGE-related compounds in canned food by ultra-performance liquid chromatography–tandem mass spectrometry

An improved analytical method enabling rapid and accurate determination and identification of bisphenol F diglycidyl ether (novolac glycidyl ether 2-ring), novolac glycidyl ether 3-ring, novolac glycidyl ether 4-ring, novolac glycidyl ether 5-ring, novolac glycidyl ether 6-ring, bisphenol A diglycidyl ether, bisphenol A (2,3-dihydroxypropyl) glycidyl ether, bisphenol A (3-chloro-2-hydroxypropyl) glycidyl ether, bisphenol A bis(3-chloro-2-hydroxypropyl) ether, and bisphenol A (3-chloro-2-hydroxypropyl) (2,3-dihydroxypropyl) ether in canned food and their contact packaging materials has been developed by using, for the first time, ultra-performance liquid chromatography coupled with tandem mass spectrometry. After comparison of electrospray ionization and atmospheric pressure chemical ionization in positive and negative-ion modes, tandem mass spectrometry with positive electrospray ionization was chosen to carry out selective multiple reaction monitoring analysis of novolac glycidyl ethers, bisphenol A diglycidyl ether, and its derivatives. The analysis time is only 5.5 min per run. Limits of detection varied from 0.01 to 0.20 ng g(-1) for the different target compounds on the basis of a signal-to-noise ratio (S/N) = 3; limits of quantitation were from 0.03 to 0.66 ng g(-1). The relative standard deviation for repeatability was <8.01%. Analytical recovery ranged from 87.60 to 108.93%. This method was successfully applied to twenty samples of canned food and their contact packaging materials for determination of migration of NOGE, BADGE, and their derivatives from can coatings into food.     

Microwave‐assisted extraction for the simultaneous determination of Novolac glycidyl ethers,bisphenol A diglycidyl ether,and its derivatives in canned food using HPLC with fluorescence detection

A microwave‐assisted extraction (MAE) protocol and an efficient HPLC analysis method were first developed for the fast extraction and simultaneous determination of bisphenol F diglycidyl ether (Novolac glycidyl ether 2‐Ring), Novolac glycidyl ether 3‐Ring, Novolac glycidyl ether 4‐Ring, Novolac glycidyl ether 5‐Ring, Novolac glycidyl ether 6‐Ring, bisphenol A diglycidyl ether, bisphenol A (2,3‐dihydroxypropyl) glycidyl ether, bisphenol A (3‐chloro‐2‐hydroxypropyl) glycidyl ether, bisphenol A bis(3‐chloro‐2‐hydroxypropyl) ether, bisphenol A (3‐chloro‐2‐hydroxypropyl) (2,3‐dihydroxypropyl) ether in canned fish and meat. After being optimized in terms of solvents, microwave power and irradiation time, MAE was selected to carry out the extraction of ten target compounds. Analytes were purified by poly(styrene‐co‐divinylbenzene) SPE columns and determinated by HPLC‐fluorescence detection. LOD varied from 0.79 to 3.77 ng/g for different target compounds based on S/N=3; LOQ were from 2.75 to 10.92 ng/g; the RSD for repeatability were <8.64%. The analytical recoveries ranged from 70.46 to 103.44%. This proposed method was successfully applied to 16 canned fish and meat, and the results acquired were in good accordance with the studies reported. Compared with the conventional liquid–liquid extraction and ultrasonic extraction, the optimized MAE approach gained the higher extraction efficiency (20–50% improved).     

Determination of bisphenol-type contaminants from food packaging materials in aqueous foods by solid-phase microextraction-high-performance liquid chromatography

A fast screening method consisting of off-line solid-phase microextraction coupled to HPLC and fluorescence detection, suitable for the analysis of several bisphenol derivatives and their degradation products in aqueous solution, has been developed. Detection limits of 0.7 ng ml(-1) for 2,2-bis[4-(glycidyloxy)phenyl]propane, 0.9 ng ml(-1) for bisphenol A bis(3-chloro-2-hydroxypropyl)ether, 1.1 ng ml(-1) for 2,2-bis(4-hydroxyphenyl)propane and 2.4 ng ml(-1) for bisphenol F diglycidyl ether have been achieved working in the linear range 10-500 ng ml(-1). The good analytical features achieved make the proposed method an interesting option for the direct determination of these compounds in aqueous canned food such as peas, tuna, olives, maize, artichokes or palm hearts. Both the optimization process and the results, including the analysis of real samples, are given and discussed.     

Quantification of derivatives of bisphenol A diglycidyl ether (BADGE) and novolac glycidyl ether (NOGE) migrated from can coatings into tuna by HPLC/fluorescence and MS detection

A reversed phase high performance liquid chromatographic method combined with fluorescence and mass spectrometric detection in series is presented for the separation and quantification of bisphenol A diglycidyl ether (BADGE) and novolac glycidyl ether (NOGE) derivatives in extracts from food can coatings, tuna and oil. Fifteen samples of tuna cans bought in four European countries were investigated. Atmospheric pressure chemical ionization mass spectrometry in the positive ion mode (APCI(+)-MS) allowed to tentatively identify BADGE and NOGE related compounds originating from reactions of the glycidyl ethers with bisphenols, phenol, butanol, water and hydrochloric acid. Quantification was based on the external standard method and fluorescence detection. Mass fractions up to 3.7 micrograms/g were found for hydrochlorination products of bisphenol F diglycidyl ether (BFDGE + 2HCl) in tuna. Furthermore, total migration quantities of phenolic ether compounds were estimated. The highest values found were 20 micrograms/g in tuna and 43 micrograms/g in the oil phase.     

Quantification of derivatives of bisphenol A diglycidyl ether (BADGE) and novolac glycidyl ether (NOGE) migrated from can coatings into tuna by HPLC/fluorescence and MS detection

A reversed phase high performance liquid chromatographic method combined with fluorescence and mass spectrometric detection in series is presented for the separation and quantification of bisphenol A diglycidyl ether (BADGE) and novolac glycidyl ether (NOGE) derivatives in extracts from food can coatings, tuna and oil. Fifteen samples of tuna cans bought in four European countries were investigated. Atmospheric pressure chemical ionization mass spectrometry in the positive ion mode (APCI(+)-MS) allowed to tentatively identify BADGE and NOGE related compounds originating from reactions of the glycidyl ethers with bisphenols, phenol, butanol, water and hydrochloric acid. Quantification was based on the external standard method and fluorescence detection. Mass fractions up to 3.7 μg/g were found for hydrochlorination products of bisphenol F diglycidyl ether (BFDGE + 2HCl) in tuna. Furthermore, total migration quantities of phenolic ether compounds were estimated. The highest values found were 20 μg/g in tuna and 43 μg/g in the oil phase. Received: 16 October 2000 / Accepted: 17 November 2000     

Accurate mass and nuclear magnetic resonance identification of bisphenolic can coating migrants and their interference with liquid chromatography/tandem mass spectrometric analysis of bisphenol A

Two unknown compounds were previously determined to be potential interferences in liquid chromatography/tandem mass spectrometry (LC/MS/MS) analysis of bisphenol A (BPA) in canned infant formula. Both yielded two identical MS/MS transitions to BPA. The identities of the unknowns were investigated using accurate mass LC/MS, LC/MS/MS, and elemental formula and structures proposed. Exact identities were confirmed through purification or synthesis followed by (1)H and (13)C nuclear magnetic resonance (NMR) experiments, as well as comparisons of one unknown with commercial standards. Comparisons of negative ion electrospray ionization (ESI) MS/MS and accurate mass spectra suggested both unknowns to be structurally identical (to BPA and each other). Positive ion ESI spectra confirmed both were larger molecules, suggesting that in the negative mode they likely fragmented to the deprotonated BPA ion in the source [corrected]. Elemental composition of positive ion accurate mass spectra and NMR analysis concluded the unknowns were oxidized forms of the known epoxy can coating monomer, bisphenol A diglycidyl ether (BADGE). One of the unknowns, 2,2-[bis-4-(2,3-dihydroxypropoxy)phenyl]propane, commonly known as BADGE*2H(2)O, is widely reported as an epoxy-phenolic can coating migrant, but has not been suggested to interfere with the MS/MS analysis of BPA. The other unknown, 2-[4-(2,3-dihydroxypropoxy)phenyl]-2-[4'-hydroxyphenyl]propane, or the oxidized form of bisphenol A monoglycidyl ether (BAMGE*H(2)O), has not been previously reported in food or packaging.     

Determination of bisphenol A diglycidyl ether and its hydrolysis and chlorohydroxy derivatives by liquid chromatography-mass spectrometry

European Legislation establishes that the sum of the migration levels of bisphenol A diglycidyl ether (BADGE), its hydrolysis (BADGE.H2O and BADGE.2H2O) and chlorohydroxy (BADGE.HCl, BADGE.2HCl and BADGE.H2O.HCl) derivatives shall not exceed the limit of 1 mg/kg in foodstuffs or food simulants. A reversed-phase high-performance liquid chromatographic (RP-HPLC) method combined with mass spectrometry detection using atmospheric pressure chemical ionisation (APCI) is developed for the separation, quantification and identification of the interesting compounds. Quantification of the analytes was carried out in the single ion recording mode, once their characteristic masses were selected from their full spectra, by using an external calibration. The optimised method was suitable for the migration evaluation of these compounds in different samples.