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超高效液相色谱-串联质谱法同时检测大米中15种常用农药的残留

黄兰淇 陈秀 张正炜 马琳 占绣萍 陈建波 赵莉

黄兰淇, 陈秀, 张正炜, 马琳, 占绣萍, 陈建波, 赵莉. 超高效液相色谱-串联质谱法同时检测大米中15种常用农药的残留[J]. 农药学学报, 2018, 20(3): 354-362. doi: 10.16801/j.issn.1008-7303.2018.0045
引用本文: 黄兰淇, 陈秀, 张正炜, 马琳, 占绣萍, 陈建波, 赵莉. 超高效液相色谱-串联质谱法同时检测大米中15种常用农药的残留[J]. 农药学学报, 2018, 20(3): 354-362. doi: 10.16801/j.issn.1008-7303.2018.0045
HUANG Lanqi, CHEN Xiu, ZHANG Zhengwei, MA Lin, ZHAN Xiuping, CHEN Jianbo, ZHAO Li. Determinationof15pesticidesresiduesinricebyultraperformanceliquidchromatography-tandemmassspectrometry[J]. Chinese Journal of Pesticide Science, 2018, 20(3): 354-362. doi: 10.16801/j.issn.1008-7303.2018.0045
Citation: HUANG Lanqi, CHEN Xiu, ZHANG Zhengwei, MA Lin, ZHAN Xiuping, CHEN Jianbo, ZHAO Li. Determinationof15pesticidesresiduesinricebyultraperformanceliquidchromatography-tandemmassspectrometry[J]. Chinese Journal of Pesticide Science, 2018, 20(3): 354-362. doi: 10.16801/j.issn.1008-7303.2018.0045

超高效液相色谱-串联质谱法同时检测大米中15种常用农药的残留

doi: 10.16801/j.issn.1008-7303.2018.0045
基金项目: 上海市农业技术推广服务中心青年人才成长计划 [沪农青字 (2016) 第4-3号]
详细信息
    作者简介:

    黄兰淇,女,硕士研究生,中级农艺师,E-mail:huanglanqi0208@126.com

    通讯作者:

    赵莉,通信作者 (Author for correspondence),女,研究员,主要从事农产品安全研究,E-mail:zhaoli5741@aliyun.com

  • 中图分类号: S481.8;TQ450.263

Determinationof15pesticidesresiduesinricebyultraperformanceliquidchromatography-tandemmassspectrometry

  • 摘要: 建立一种超高效液相色谱-串联质谱同时检测大米中甲氨基阿维菌素苯甲酸盐等15种常用农药残留的方法,考察了基质效应、提取溶剂种类、提取方法以及不同净化方法对15种农药回收率的影响。样品经V (乙腈) : V (丙酮) : V (水) = 16 : 2 : 2混合溶液匀浆提取,分散固相萃取法净化,电喷雾正离子 (ESI+) 模式电离,多反应监测 (MRM) 模式检测,外标法定量。结果表明:在0.005~1 mg/L范围内,甲氨基阿维菌素苯甲酸盐等15种农药的质量浓度与对应的峰面积间线性关系良好,相关系数 (r) ≥ 0.99;在0.01、0.1、1和4 mg/kg 4个添加水平下,15种农药在大米中的平均回收率在82%~116%之间,相对标准偏差在1.2%~12%之间 (n = 5)。方法检出限为0.000 5~0.005 mg/kg,定量限为0.01 mg/kg。用该方法对上海市郊20个批次的大米样品进行测定,均未检出农药残留超标。该方法操作简单、快速、准确,适用于大米中甲氨基阿维菌素苯甲酸盐等15种常用农药残留的同时检测。
  • 图  1  0.1%甲酸-水/甲醇 (A) 和0.1%甲酸-水/乙腈 (B) 体系下吡蚜酮提取色谱图

    Figure  1.  Extraction chromatogram of pymetrozine in 0.1% formic acid-water/methanol (A) and 0.1% formic acid-water/acetonitrile (B)

    图  2  15种农药总离子流图

    1-吡蚜酮pymetrozine;2-呋虫胺dinotefuran;3-烯啶虫胺nitenpyram;4-噻虫嗪thiamethoxam;5-吡虫啉imidacloprid;6-噻虫胺clothianidin;7-三环唑tricyclazole;8-氯虫苯甲酰胺chlorantraniliprole;9-嘧菌酯azoxystrobin;10-噻呋酰胺thifluzamide;11A-多杀霉素A spinosad A;11D-多杀霉素D spinosad D;12-戊唑醇tebuconazole;13-甲氨基阿维菌素苯甲酸盐emamectin benzoate;14-茚虫威indoxacarb;15-噻嗪酮buprofezin。

    Figure  2.  Total ion chromatogram (TIC) of the 15 pesticides

    图  3  不同提取溶剂下15种目标农药在大米中回收率对比结果 (添加水平为0.1 mg/kg)

    1-吡虫啉imidacloprid;2-吡蚜酮pymetrozine;3-A多杀霉素A spinosad A;3-D多杀霉素D spinosad D;4-呋虫胺dinotefuran;5-甲氨基阿维菌素苯甲酸盐emamectin benzoate;6-氯虫苯甲酰胺chlorantraniliprole;7-嘧菌酯azoxystrobin;8-噻虫胺clothianidin;9-噻虫嗪thiamethoxam;10-噻呋酰胺thifluzamide;11-噻嗪酮buprofezin;12-三环唑tricyclazole;13-戊唑醇tebuconazole;14-烯啶虫胺nitenpyram;15-茚虫威indoxacarb。

    Figure  3.  The comparison of the recoveries of 15 pesticides in rice under the different solvent conditions (spiked 0.1 mg/kg)

    图  4  不同提取方法下15种目标农药在大米中回收率对比结果 (添加水平为0.1 mg/kg)

    1-吡虫啉imidacloprid;2-吡蚜酮pymetrozine;3-A多杀霉素A spinosad A;3-D多杀霉素D spinosad D;4-呋虫胺dinotefuran;5-甲氨基阿维菌素苯甲酸盐emamectin benzoate;6-氯虫苯甲酰胺chlorantraniliprole;7-嘧菌酯azoxystrobin;8-噻虫胺clothianidin;9-噻虫嗪thiamethoxam;10-噻呋酰胺thifluzamide;11-噻嗪酮buprofezin;12-三环唑tricyclazole;13-戊唑醇tebuconazole;14-烯啶虫胺nitenpyram;15-茚虫威indoxacarb。

    Figure  4.  The comparison of the recoveries of 15 pesticides in rice under the different extractionconditions (spiked 0.1 mg/kg)

    图  5  5种不同净化方法对15种目标农药回收率的影响 (添加水平为0.1 mg/kg)

    1-吡虫啉imidacloprid;2-吡蚜酮pymetrozine;3-A多杀霉素A spinosad A;3-D多杀霉素D spinosad D;4-呋虫胺dinotefuran;5-甲氨基阿维菌素苯甲酸盐emamectin benzoate;6-氯虫苯甲酰胺chlorantraniliprole;7-嘧菌酯azoxystrobin;8-噻虫胺clothianidin;9-噻虫嗪thiamethoxam;10-噻呋酰胺thifluzamide;11-噻嗪酮buprofezin;12-三环唑tricyclazole;13-戊唑醇tebuconazole;14-烯啶虫胺nitenpyram;15-茚虫威indoxacarb

    Figure  5.  The effect of five different purification methods on the recoveries of 15 pesticides (spiked 0.1 mg/kg)

    图  6  大米实际样品中吡虫啉和三环唑的总离子流图

    Figure  6.  Total ion chromatogram of imidacloprid and tricyclazole in a real rice sample

    表  1  15种农药质谱采集参数

    Table  1.   Mass spectrum acquisition parameters of 15 pesticides

    农药
    Pesticide
    母离子
    Precursor ion, m/z
    子离子
    Product ions, m/z
    碰撞电压
    Fragmentor/V
    碰撞能量
    Collision energy/V
    吡蚜酮 pymetrozine 218.3 105.2* 80 23
    79.0 80 23
    呋虫胺 dinotefuran 203.1 129.0* 90 12
    114.0 90 10
    烯啶虫胺 nitenpyram 271.0 237.0* 100 15
    224.0 100 15
    噻虫嗪 thiamethoxam 292.0 211.0* 80 10
    181.0 80 20
    吡虫啉 imidacloprid 256.1 209.0* 80 10
    175.0 80 10
    噻虫胺 clothianidin 250.0 169.0* 90 5
    132.0 90 5
    三环唑 tricyclazole 189.7 135.7 30 26
    162.7* 30 22
    氯虫苯甲酰胺 chlorantraniliprole 484.0 453.0* 120 17
    286.0 120 23
    嘧菌酯 azoxystrobin 404.1 372.0* 120 10
    344.0 120 15
    噻呋酰胺 thifluzamide 526.8 168.0* 100 25
    148.0 100 25
    多杀霉素 A spinosad A 732.5 142.1* 140 35
    98.0 140 55
    多杀霉素 D spinosad D 746.5 142.1* 140 35
    98.0 140 55
    戊唑醇 tebuconazole 308.2 124.8* 120 30
    70.0 120 40
    甲氨基阿维菌素苯甲酸盐 emamectin benzoate 886.2 158.2* 200 40
    126.1 200 50
    茚虫威 indoxacarb 528.0 249.0* 120 15
    218.0 120 20
    噻嗪酮 buprofezin 306.2 201.1* 120 15
    116.1 120 10
    *定量离子 (Quantitative ion)。
    下载: 导出CSV

    表  2  溶剂和基质标准样品的标准曲线、检出限及斜率比值

    Table  2.   Standards curves and LODs of 15 pesticides in solvent and matrix and their slope ratios

    农药 Pesticide溶剂 Solvent基质 Matrix斜率比
    Ratio of slope
    检出限
    LOD/(mg/kg)
    线性方程
    Linear equation
    相关系数
    r
    线性方程
    Linear equation
    相关系数
    r
    吡蚜酮 pymetroziney = 827 150x + 1 6230.999 0y = 714 658x + 1 753.80.999 90.864 00.001
    呋虫胺 dinotefurany = 35 666x + 759.090.995 8y = 19 349x + 1830.999 70.542 50.005
    烯啶虫胺 nitenpyramy = 67 218x + 1 6040.995 0y = 83 265x + 1 4220.998 91.239 00.005
    噻虫嗪 thiamethoxamy = 50 155x + 1 2150.994 4y = 37 501x + 6020.998 80.747 70.005
    吡虫啉 imidaclopridy = 46 688x + 3820.998 2y = 29 524x + 8.1580.999 90.632 40.005
    噻虫胺 clothianidiny = 27 074x + 2320.997 9y = 14 451x + 210.999 80.533 80.005
    三环唑 tricyclazoley = 78 356x + 1 4090.996 1y = 78 982x + 4120.999 91.008 00.005
    氯虫苯甲酰胺
    chlorantraniliprole
    y = 16 318x + 2850.994 2y = 15 142x + 1710.998 70.927 90.005
    嘧菌酯 azoxystrobiny = 454 071x + 9 0510.995 2y = 313 989x + 3 2640.999 50.691 50.001
    噻呋酰胺 thifluzamidey = 3 751x + 620.997 3y = 1 901x – 110.999 10.506 80.005
    多杀霉素 A spinosad Ay = 968 735x + 10 3620.998 0y = 1 000 000x + 2 030.80.999 91.032 00.005
    多杀霉素 D spinosad Dy = 172 804x + 1900.999 6y = 192 931x – 1 210.40.999 71.117 00.005
    戊唑醇 tebuconazoley = 330 633x + 1 1920.999 2y = 201 355x – 1 2020.999 70.609 00.005
    甲氨基阿维菌素苯甲酸盐
    emamectin benzoate
    y = 213 488x + 3 7850.996 7y = 382 367x – 1180.999 91.791 00.005
    茚虫威 indoxacarby = 3 803x + 1460.995 4y = 1 987x + 90.999 10.522 50.005
    噻嗪酮 buprofeziny = 2 000 000x + 39 2370.997 8y = 2 000 000x + 29 8880.999 91.000 00.000 5
    下载: 导出CSV

    表  3  15种农药在大米中的平均添加回收率和相对标准偏差

    Table  3.   The average recoveries and relative standard deviations (RSDs) of 15 pesticides in rice at 4 spiked levels

    农药
    Pesticide
    添加水平 Spiked level/(mg/kg)
    0.01 0.1 1 4
    回收率
    Recovery /%
    相对标准偏差
    RSD/%
    回收率
    Recovery /%
    相对标准偏差
    RSD/%
    回收率
    Recovery/%
    相对标准偏差
    RSD/%
    回收率
    Recovery/%
    相对标准偏差
    RSD/%
    吡蚜酮 pymetrozine 102 7.2 84 4.1 89 2.2 99 3.3
    呋虫胺 dinotefuran 103 8.6 101 2.5 105 1.8 99 8.4
    烯啶虫胺 nitenpyram 84 7.5 82 3.5 86 3.3 99 5.6
    噻虫嗪 thiamethoxam 112 5.9 107 3.3 109 1.6 100 4.4
    吡虫啉 imidacloprid 106 4.5 110 4.5 112 1.2 96 1.4
    噻虫胺 clothianidin 109 5.9 108 4.6 100 1.7 99 2.3
    三环唑 tricyclazole 98 7.6 107 2.7 106 2.3 106 6.4
    氯虫苯甲酰胺 chlorantraniliprole 106 11 112 2.9 105 4.8 84 6.9
    嘧菌酯 azoxystrobin 95 7.8 112 1.9 113 1.7 102 5.9
    噻呋酰胺 thifluzamide 106 9.0 111 12 110 2.1 113 5.6
    多杀霉素 A spinosad A 100 6.5 112 2.6 107 1.7 105 5.4
    多杀霉素 D spinosad D 107 8.9 113 4.9 108 1.7 102 5.7
    戊唑醇 tebuconazole 101 9.1 109 4.3 114 1.3 93 3.3
    甲氨基阿维菌素苯甲酸盐 emamectin benzoate 106 4.8 108 4.6 116 3.8 97 7.4
    茚虫威 indoxacarb 106 12 102 10 109 4.5 104 6.7
    噻嗪酮 buprofezin 111 4.5 112 5.7 104 2.2 102 2.7
    下载: 导出CSV

    表  4  15种目标农药在大米实际样品中的残留量

    Table  4.   Analytical results of 15 pesticides residues in rice samples

    农药
    Pesticide
    检出浓度
    Concentration/(mg/kg)
    最大残留限量[21]
    MRLs/(mg/kg)
    吡蚜酮 pymetrozine - 0.2
    呋虫胺 dinotefuran - 1
    烯啶虫胺 nitenpyram - 0.1
    噻虫嗪 thiamethoxam - 0.1
    吡虫啉 imidacloprid 0.023~0.043 0.05
    噻虫胺 clothianidin - 0.2
    三环唑 tricyclazole 0.011~0.023 2
    氯虫苯甲酰胺 chlorantraniliprole - 0.5
    嘧菌酯 azoxystrobin - 0.5
    噻呋酰胺 thifluzamide - 3
    多杀霉素 A spinosad A - 1
    多杀霉素 D spinosad D - 1
    戊唑醇 tebuconazole - 0.5
    甲氨基阿维菌素苯甲酸盐 emamectin benzoate - 0.02
    茚虫威 indoxacarb - 0.1
    噻嗪酮 buprofezin - 0.3
    -: 未检出 (not detected)。
    下载: 导出CSV
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出版历程
  • 收稿日期:  2018-01-03
  • 录用日期:  2018-04-16
  • 刊出日期:  2018-06-30

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