Determination of Diphenylamine Residue in Milk Powder by Gas Chromatography-Mass Spectrometry with Carb/NH2 Solid Phase Extraction Purification
摘 要
针对国家标准方法GB/T 23210-2008测定乳粉中二苯胺残留量时假阳性率高等现象,提出了题示方法,并进行气相色谱-串联质谱法(GC-MS/MS)确证、回收试验以及基质效应试验,比较了十八烷基键合硅胶固相萃取柱(C18小柱)、弗罗里硅土固相萃取柱(Florisil小柱)和石墨化碳黑-氨基复合固相萃取柱(Carb/NH2小柱)对实际样品的净化效果。在3 g乳粉样品中加入20 mL乙腈和5 g氯化钠,均质2 min,离心5 min,重复提取一次。合并上清液于50 mL鸡心瓶中,于40℃旋蒸至1 mL,过预先活化好的Carb/NH2小柱,收集流出液。用体积比3∶1乙腈-甲苯混合溶液5 mL洗涤上述鸡心瓶,洗涤液过柱,再加入体积比3∶1乙腈-甲苯混合溶液20 mL洗脱柱子。净化过程控制流出速率为1 mL·min-1,合并全部流出液,于40℃旋蒸至近干,氮气吹干,用1 mL乙酸乙酯溶解后用气相色谱-质谱法测定。结果显示:以C18小柱净化10种市售乳粉样品时,二苯胺的阳性率为100%,二级质谱结果显示,质荷比(m/z)169,167,168(二苯胺的定量及定性离子)处对应的物质为样品溶液中的干扰物质,说明国家标准方法检测结果呈假阳性;Florisil小柱所得样品溶液中干扰物较多,二苯胺回收率偏高,且显示出强基质效应;Carb/NH2小柱净化效果好,且不需要基质匹配法定量,所得二苯胺的质量浓度在0.01~1.00 mg·L-1内与其对应的峰面积呈线性关系,检出限为3.4 μg·kg-1。对空白乳粉样品进行3个浓度水平的加标回收试验,回收率为84.6%~93.1%,测定值的相对标准偏差(n=6)为4.2%~7.5%。方法用于以上10种市售乳粉样品的分析,均未检出二苯胺的残留。
Abstract
The method shown in the title was proposed based on the fact of high false positive rate of diphenylamine residue in milk powder by the national standard method of GB/T 23210-2008. Tests for confirmation with gas chromatography-tandem mass spectrometry (GC-MS/MS), recovery and matrix effect were made, to compare purification effects of C18 cartridge, Florisil cartridge and Carb/NH2 cartridge on the actual samples. Milk powder sample (3 g) was homogenized with 20 mL of acetonitrile and 5 g of sodium chloride for 2 min, and centrifuged for 5 min, and the extraction was repeated once again. The supernatants obtained were combined to a heart-shaped pendant (50 mL), and evaporated by rotation to 1 mL at 40 ℃. The above solution was passed through the Carb/NH2 cartridge activated beforehand, and the effluent was collected. Acetonitrile-toluene mixed solution (15 mL) at volume ratio of 3∶1 was used to wash the heart-shaped pendant, and the rinsing solution was loaded on the Carb/NH2 cartridge. Acetonitrile-toluene mixed solution (20 mL) at volume ratio of 3∶1 was taken, and passed through the Carb/NH2 cartridge for elution. Throughout the purification process, the effluence flow was controlled at 1 mL·min-1. The collected eluate was combined, evaporated by rotation to nearly dry at 40 ℃, and dried by nitrogen. The residue was dissolved with 1 mL of ethyl acetate, and the solution was analyzed by gas chromatography-mass spectrometry. It was shown that the positive rate of diphenylamine was 100% when the 10 commercial milk powder samples were purified with C18 cartridge, and the corresponding substances at m/z 169, 167, 168 (quantitative and qualitative ions of diphenylamine) were interfering substances in the sample solution which was confirmed by MS/MS, and it was concluded that the results provided by the national standard method were false positive. When purified with Florisil cartridge, many interferents in the sample solution were detected, with high recovery and strong matrix effect. When purified with Carb/NH2 cartridge, the purification effect was better, and matrix matching method was not needed for quantification. Linear relationship between values of mass concentration and peak area of diphenylamine was kept in the range of 0.01-1.00 mg·L-1, with detection limit of 3.4 μg·kg-1. Test for the spiked recovery was made at the 3 concentration levels with negative milk powder sample as matrix, giving recoveries in the range of 84.6%-93.1%, and RSDs (n=6) of the determined values ranged from 4.2% to 7.5%. This method was applied to the analysis of the 10 milk powder samples described above, and the residues of diphenylamine were not detected.
中图分类号 O657.63 DOI 10.11973/lhjy-hx202208004
所属栏目 工作简报
基金项目 国家重点研发计划项目(2019YFC1606503)
收稿日期 2021/8/8
修改稿日期
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备注安红梅,高级工程师,硕士,研究方向为食品安全,sunyong2030@163.com
引用该论文: AN Hongmei,WANG Lijuan,LI Chunyang,HE Huiyuan,XIE Jingjing. Determination of Diphenylamine Residue in Milk Powder by Gas Chromatography-Mass Spectrometry with Carb/NH2 Solid Phase Extraction Purification[J]. Physical Testing and Chemical Analysis part B:Chemical Analysis, 2022, 58(8): 888~892
安红梅,王丽娟,李春扬,何蕙园,谢精精. Carb/NH2固相萃取柱净化-气相色谱-质谱法测定乳粉中二苯胺的残留量[J]. 理化检验-化学分册, 2022, 58(8): 888~892
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参考文献
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【3】中华人民共和国国家卫生健康委员会,农业农村部,国家市场监督管理总局.食品安全国家标准食品中农药最大残留限量:GB 2763-2021[S].北京:中国农业出版社, 2021.
【4】邓小娟,李文斌,晋立川,等.QuEChERS-气相色谱法测定牛奶中24种有机氯及菊酯类农药残留[J].食品科学, 2016,37(18):141-145.
【5】WU Z F.Determination of 19 organochlorine pesticides residues in milk powder by GPC-GC-MS[J].International Journal of Nutrition and Food Sciences, 2018,7(4):129-133.
【6】林竹光,陈美瑜,张莉莉,等.气相色谱-负离子化学源质谱法分析牛奶饮品和奶粉中19种有机磷农药残留[J].分析测试学报, 2007,26(3):331-334.
【7】付文雯,罗彤,朱影,等.QuEChERS-气相色谱-串联质谱测定牛奶中有机氯农药及多氯联苯的分析[J].食品科学, 2018,39(8):309-313.
【8】陈美瑜,林竹光.牛奶中32种农药的气相色谱-离子阱串联质谱法测定[J].分析测试学报, 2019,38(2):182-187.
【9】郑军红.LC-MS/MS测定牛奶和奶粉中多种农药残留量的研究[D].泰安:山东农业大学, 2009.
【10】GOLGE O, KOLUMAN A, KABAK B.Validation of a modified QuEChERS method for the determination of 167 pesticides in milk and milk products by LC-MS/MS[J].Food Analytical Methods, 2018,11(4):1122-1148.
【11】中华人民共和国国家质量监督检验检疫总局,中国国家标准化管理委员会.牛奶和奶粉中511种农药及相关化学品残留量的测定气相色谱-质谱法:GB/T 23210-2008[S].北京:中国标准出版社, 2009.
【12】中华人民共和国国家质量监督检验检疫总局,中国国家标准化管理委员会.牛奶和奶粉中493种农药及相关化学品残留量的测定液相色谱-串联质谱法:GB/T 23211-2008[S].北京:中国标准出版社, 2009.
【13】安红梅,柯润辉,王丽娟,等.固相萃取-气相色谱-火焰光度法同时测定植物性肽粉中42种有机磷农药残留[J].食品与发酵工业, 2018,44(6):245-250.
【14】中华人民共和国国家质量监督检验检疫总局,中国国家标准化管理委员会.实验室质量控制规范食品理化检测:GB/T 27404-2008[S].北京:中国标准出版社, 2008.
【15】王敬,艾连峰,马育松,等.气相色谱/三重四极杆串联质谱法测定牛奶及奶粉中213种农药多残留[J].色谱, 2015,33(11):1175-1185.
【16】刘慧慧,张华威,魏潇,等.超高效液相色谱-串联质谱法测定水产品中13种磺酰脲类除草剂残留量[J].分析化学, 2018,46(3):386-392.
【17】秦富,邓全道,李湧,等.液相色谱-串联质谱法测定月柿中187种农药残留[J].分析测试学报, 2018,37(8):879-886.
【18】KITTLAUS S, SCHIMANKE J, KEMPE G, et al.Assessment of sample cleanup and matrix effects in the pesticide residue analysis of foods using postcolumn infusion in liquid chromatography-tandem mass spectrometry[J].Journal of Chromatography A, 2011,1218(46):8399-8410.
【19】TRIPATHY V, SHARMA K K, YADAV R, et al.Development, validation of QuEChERS-based method for simultaneous determination of multiclass pesticide residue in milk, and evaluation of the matrix effect[J].Journal of Environmental Science and Health.Part.B, Pesticides, Food Contaminants, and Agricultural Wastes, 2019,54(5):394-406.
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