CEN TR 15641-2007 Food analysis - Determination of pesticide residues by LCMS MS - Tandem mass spectrometric parameters《食品分析 用LC-MS MS测定农药残留物 串联质谱测定参数》.pdf

《CEN TR 15641-2007 Food analysis - Determination of pesticide residues by LCMS MS - Tandem mass spectrometric parameters《食品分析 用LC-MS MS测定农药残留物 串联质谱测定参数》.pdf》由会员分享，可在线阅读，更多相关《CEN TR 15641-2007 Food analysis - Determination of pesticide residues by LCMS MS - Tandem mass spectrometric parameters《食品分析 用LC-MS MS测定农药残留物 串联质谱测定参数》.pdf（26页珍藏版）》请在麦多课文档分享上搜索。

1、PUBLISHED DOCUMENTPD CEN/TR 15641:2007Food analysis Determination of pesticide residues by LC-MS/MS Tandem mass spectrometric parametersICS 67.050g49g50g3g38g50g51g60g44g49g42g3g58g44g55g43g50g56g55g3g37g54g44g3g51g40g53g48g44g54g54g44g50g49g3g40g59g38g40g51g55g3g36g54g3g51g40g53g48g44g55g55g40g39g3

2、g37g60g3g38g50g51g60g53g44g42g43g55g3g47g36g58PD CEN/TR 15641:2007This Published Document was published under the authority of the Standards Policy and Strategy Committee on 28 September 2007 BSI 2007ISBN 978 0 580 58353 7National forewordThis Published Document is the UK implementation of CEN/TR 15

3、641:2007.The UK participation in its preparation was entrusted to Technical Committee AW/-/3, Food analysis Horizontal methods.A list of organizations represented on this committee can be obtained on request to its secretary.This publication does not purport to include all the necessary provisions o

4、f a contract. Users are responsible for its correct application.Amendments issued since publicationAmd. No. Date CommentsTECHNICAL REPORTRAPPORT TECHNIQUETECHNISCHER BERICHTCEN/TR 15641August 2007ICS 67.050English VersionFood analysis - Determination of pesticide residues by LC-MS/MS - Tandem mass s

5、pectrometric parametersAnalyse des produits alimentaires - Dtermination desrsidus de pesticides par CL-SM/SM - Paramtres despectromtrie de masse en tandemLebensmitteluntersuchung - Bestimmung vonPestizidrckstnden mit LC-MS/MS - Parameter fr dieTandem-MassenspektrometrieThis Technical Report was appr

6、oved by CEN on 25 July 2007. It has been drawn up by the Technical Committee CEN/TC 275.CEN members are the national standards bodies of Austria, Belgium, Bulgaria, Cyprus, Czech Republic, Denmark, Estonia, Finland,France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembo

7、urg, Malta, Netherlands, Norway, Poland, Portugal,Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland and United Kingdom.EUROPEAN COMMITTEE FOR STANDARDIZATIONCOMIT EUROPEN DE NORMALISATIONEUROPISCHES KOMITEE FR NORMUNGManagement Centre: rue de Stassart, 36 B-1050 Brussels 2007 CEN All rights of

8、 exploitation in any form and by any means reservedworldwide for CEN national Members.Ref. No. CEN/TR 15641:2007: E2 Contents Page Foreword3 Introduction .4 1 Scope 5 2 Analyte specific parameters for selective reaction monitoring of pesticides.5 2.1 General5 2.2 LC Parameters6 2.3 General MS/MS par

9、ameters 6 2.4 Analyte specific MS/MS Parameters7 Bibliography 23 CEN/TR 15641:20073 Foreword This document (CEN/TR 15641:2007) has been prepared by Technical Committee CEN/TC 275 “Food analysis - Horizontal methods”, the secretariat of which is held by DIN. CEN/TR 15641:20074 Introduction Pesticide

10、residue analysis employs multi methods involving extraction of residues from foods and clean up of the extract to obtain as many pesticide residues as possible in the purified extracts. Afterwards the extracts can be analysed by different kinds of instruments. The hyphenation of liquid chromatograph

11、y (LC) and tandem mass spectrometry (MS/MS) has become one of the most universal, but selective and sensitive analysis techniques for identification and quantification of pesticide residues in extracts of foods. For the ionization of the analytes (M) in LC-MS/MS, electro spray ionization (ESI) or at

12、mospheric pressure chemical ionization (APCI) interfaces are most commonly used. Depending on the selected polarity of the ionization, protonated or deprotonated molecular ions like M+H+or M-H-are generated. Using ESI, relatively stable adducts (clusters) of the analytes (M) and components of the mo

13、bile phase like ions (e.g. ammonium, sodium or potassium ions) or solvent molecules (e.g. methanol) can be additionally formed. To obtain a high yield of quasi molecular ions and therefore to increase the sensitivity of the measurement these clusters have to be broken. When using ESI the formed addu

14、cts are accelerated by a potential (e.g. declustering potential or cone voltage) in the ion source at atmospheric pressure. Due to collision with neutral gas molecules the clusters (adducts) are broken in the ion source. Under certain conditions some adduct-ions formed are stable (e.g. with ammonium

15、 cation M+NH4+). It should be mentioned, however, that ammonium adducts are usually not generated in the APCI-mode and that their formation when using ESI strongly depends on the concentration of ammonium ions in the LC mobile phase. Adduct ions like M+NH4+ can also be used alternatively for quantif

16、ication if they were shown to provide reproducible signals. Sodium adducts are usually not suitable for quantitative analysis as their formation and decomposition tends to be highly irreproducible. The selective determination of each target compound is performed by acquisition of characteristic prod

17、uct ions of the precursor ion (quasi molecular ion or adduct) in the selected reaction monitoring (SRM). Decomposition of the precursor ions in the collision cell is induced by collision with molecules of the collision gas (nitrogen or argon). The collision energy (CE) necessary for fragmentation is

18、 a very substantial parameter of the MS/MS optimization for maximum sensitivity. If LC-MS/MS measurement should be used not only for quantification but also for confirmation of positive findings, at least two SRM transitions have to be recorded. CEN/TR 15641:20075 1 Scope This Technical Report lists

19、 mass spectrometric parameters which are useful for the application of European Standards for the determination of pesticide residues in foods of plant origin that use LC-MS/MS, such as the standards in preparation: prEN 15637 “Foods of plant origin Determination of pesticide residues using LC-MS/MS

20、 following methanol extraction and clean up using diatomaceous earth“ prEN 15662 “Foods of plant origin Determination of pesticide residues using GC-MS and/or LC-MS/MS following acetonitrile extraction/partitioning by dispersive SPE QuEChERS-method” To facilitate the determination of active substanc

21、es and/or metabolites using LC-MS/MS, Table 1 specifies the precursor ions and product ions suitable for quantification, which can be used independently of the type of triple quadrupole mass spectrometer. However, using an ion trap mass spectrometer other product ions can be generated or at least th

22、e relative intensities of the ions are different to triple quadrupole instruments. Furthermore, the additional parameters declustering potential (DP), collision energy (CE), relative retention times and an approximate classification of detection sensitivity are presented in Table 1. These were deriv

23、ed using the API 20001)and should be applicable at least for other instruments of the API type (Applied Biosystems). 2 Analyte specific parameters for selective reaction monitoring of pesticides 2.1 General All values indicated in Table 2 were acquired using the above mentioned LC-MS/MS system under

24、 the experimental conditions as outlined in 2.2. Comparative investigations showed that these parameters can be transferred simply on instruments of other types of the same manufacturer or after adjustment also on devices of other manufacturers (see in 2.3) 1)Instruments of the API type are products

25、 supplied by Applied Biosystems (Foster City, CA, USA). This information is given for the convenience of users of this Technical Report and does not constitute an endorsement by CEN of the product named. Equivalent products may be used if they can be shown to lead to the same results. CEN/TR 15641:2

26、0076 2.2 LC Parameters The following LC operating conditions have been proven to be satisfactory. This is an example for appropriate experimental conditions. Equivalent conditions may be used if they can be shown to lead to the same results. HPLC pump HP11002)Binary Pump (G1312A) Autosampler HP1100(

27、G1313A) Injection volume 20 l Column Phenomenex3)Aqua 5 C18 125 , 50 mm 2 mm Mobile phase A Methanol/water 2+8 (V/V) with 5 mmol/l ammonium formate Mobile phase B Methanol/water 9+1 (V/V) with 5 mmol/l ammonium formate Flow rate 0,2 ml/min Column temperature 20 C Gradient Linear: 0 min 0 % B 11 min

28、100 % B 23 min 100 % B 25 min 0 % B 36 min 0 % B (equilibration time) As slight fluctuations in the measurement conditions influence the retention time, usually relative retention times (RRT), related to a standard substance, are compared. The standard substance for the calculation of the RRT values

29、 in Table 1 was Imazalil (RRT = 1,000). It could be shown that the use of other mobile phase systems does not shift the order of elution substantially, except for those compounds which are sensitive to the pH of eluent. Often retention data can be transferred to HPLC columns of other manufacturers,

30、if a typical reversed phase is used. 2.3 General MS/MS parameters The following general MS/MS operating conditions have been proven to be satisfactory. This is an example for appropriate experimental conditions. Equivalent conditions may be used if they can be shown to lead to the same results MS/MS

31、 instrument Applied Biosystems API 2000Ion source Turbo Ion Spray(ESI) 2)Instruments of the HP type are products supplied by Agilent Technologies Inc. (Palo Alto, CA, USA). This information is given for the convenience of users of this Technical Report and does not constitute an endorsement by CEN o

32、f the product named. Equivalent products may be used if they can be shown to lead to the same results. 3)HPLC columns of the Aqua type are products supplied by Phenomenex (Torrance, CA, USA). This information is given for the convenience of users of this Technical Report and does not constitute an e

33、ndorsement by CEN of the product named. Equivalent products may be used if they can be shown to lead to the same results. CEN/TR 15641:20077 Table 1 Ion source and general parameters Ion polarity positive Gas 2 temperature 400 C Curtain gas nitrogen, 35 psi (241 kPa) Resolution MS 1 unit Collision g

34、as nitrogen, 2 arbitrary units Resolution MS 2 unit Ion spray voltage 5500 V Dwell time 25 ms Gas 1 nitrogen, 60 psi (414 kPa) Focusing potential 360 V Gas 2 nitrogen, 60 psi (414 kPa) 2.4 Analyte specific MS/MS Parameters The analyte specific parameters for selective reaction monitoring of pesticid

35、es are listed in Table 1 1. The names of the individual analytes are supplemented by the CAS number (Chemical Abstracts Service), which is useful for the search in databases. It is usually taken from 2, but there can be several numbers in individual cases, e.g. for isomers and racemates. The values

36、for the declustering potential (DP), indicated in Table 1 for the API 2000, have to be increased by 20 V for tandem mass spectrometers of the type API 3000or API 4000. It is to be considered that DP breaks not only the clusters but can already induce fragmentation of the precursor ions (at too high

37、values) in the ESI source before entering into the first MS. NOTE It is not necessary to change the collision energy for API 3000or API 4000instruments as the differences for the CE are less than 5 V. When using tandem mass spectrometers of other manufacturers the correct value for the collision ene

38、rgy should be determined in tuning experiments for analytes with particularly low and high collision energy since it has relevant influence on the intensity of the SRM transition. Based on these data, in a first approximation the values for the collision energy of further pesticides can be derived p

39、roportionally from the data in the table and the observed difference (difference of CE at instrument X to the API 2000). The values of the declustering potential (other name “cone voltage”) for other instruments have to be determined individually. On the intensity of the SRM transitions this paramet

40、er has a smaller influence than the collision energy. Table 2 MS/MS Parameters of 497 analytes Pesticide (Metabolite) 1stSRM 2ndSRM CAS No. Ionization Quasi molecular ion Q1Mass(amu)Declustering potential(V) Q3Mass(amu)Collisionenergy(V) Q3Mass(amu)Collisionenergy(V) Relative retentionon endcapped R

41、Pphase a )Sensitivityof detection b 2,4-D 94-75-7 ESI - M-H- 219,0 -21 160,9 -14 124,9 -34 0,69 * 2,4-DB 94-82-6 ESI - M-H- 247,0 -66 160,8 -12 124,9 -34 0,86 * 2-Naphthyloxyacetic acid 120-23-0 ESI + M+NH4+ 220,1 36 157,1 19 127,1 43 0,66 n.a. 2-Naphthyloxyacetic acid 120-23-0 ESI - M-H- 201,1 -71

42、143,0 -18 114,9 -50 0,66 * 3,4,5-Trimethacarb 2686-99-9 ESI + M+H+ 194,1 61 137,1 15 122,0 35 0,86 * 4-CPA 122-88-3 ESI - M-H- 185,0 -71 126,8 -18 140,7 -12 0,47 * Acephate 30560-19-1 ESI + M+H+ 184,1 6 124,9 25 142,9 13 0,11 * Acetamiprid 135410-20-7 ESI + M+H+ 223,0 36 126,0 27 90,1 45 0,58 * CEN/

43、TR 15641:20078 Pesticide (Metabolite) 1stSRM 2ndSRM CAS No. Ionization Quasi molecular ion Q1Mass(amu)Declustering potential (V) Q3Mass(amu)Collisionenergy(V) Q3Mass(amu)Collisionenergy(V) Relative retentionon endcapped RPphase a )Sensitivityof detection b Acibenzolar-S-methyl 135158-54-2 ESI + M+H+

44、 210,9 26 136,1 39 140,0 31 0,92 * Aclonifen 74070-46-5 ESI + M+H+ 265,0 56 182,1 39 218,0 33 0,99 * Acrinathrin 101007-06-1 ESI + M+NH4+ 559,1 26 208,1 23 181,1 43 1,20 * Alachlor 15972-60-8 ESI + M+H+ 270,1 31 238,1 15 162,2 25 0,97 * Aldicarb 116-06-3 ESI + M+NH4+ 208,1 1 89,1 21 116,0 13 0,66 *

45、Aldicarb-sulfoxide 1646-87-3 ESI + M+H+ 207,1 36 89,1 17 131,9 11 0,15 * Aldoxycarb 1646-88-4 ESI + M+NH4+ 240,1 11 148,0 19 86,1 27 0,19 * Alloxydim 55634-91-8 ESI + M+H+ 324,2 11 178,3 27 234,2 19 0,77 * Ametryn 834-12-8 ESI + M+H+ 228,1 36 186,2 25 96,1 35 0,90 * Amidosulfuron 120923-37-7 ESI + M

46、+H+ 370,0 21 217,9 31 260,9 19 0,46 * Aminocarb 2032-59-9 ESI + M+H+ 209,1 16 152,1 19 137,2 31 0,74 * Amitraz 33089-61-1 ESI + M+H+ 294,2 16 163,1 21 122,1 41 1,19 * Amitrole 61-82-5 ESI + M+H+ 85,0 51 58,2 29 57,0 23 0,07 * Aramit 140-57-8 ESI + M+NH4+ 352,1 41 191,2 19 105,0 57 1,09 * Atrazine 19

47、12-24-9 ESI + M+H+ 216,1 21 174,0 25 103,9 27 0,83 * Atrazine, 2-hydroxy- 2163-68-0 ESI + M+H+ 198,1 66 69,0 47 156,2 25 0,65 * Atrazine, desethyl- 6190-65-4 ESI + M+H+ 188,1 56 104,0 33 146,0 25 0,59 * Atrazine, desethyl-2-hydroxy- 6190-65-4 ESI + M+H+ 170,1 66 128,1 23 86,0 31 0,14 * Atrazine, des

48、isopropyl- 1007-28-9 ESI + M+H+ 174,1 56 104,2 31 96,0 27 0,39 * Avermectin B1a 65195-55-3 ESI + M+NH4+ 890,5 41 305,1 35 145,2 43 1,33 * Avermectin B1b 65195-56-4 ESI + M+NH4+ 876,5 41 291,1 35 145,2 43 1,26 * Azaconazole 60207-31-0 ESI + M+H+ 300,0 56 231,0 23 159,0 37 0,86 * Azamethiphos 35575-96

49、-3 ESI + M+H+ 325,0 16 183,0 21 139,2 33 0,74 * Azimsulfuron 120162-55-2 ESI + M+H+ 425,1 31 182,1 23 156,1 43 0,55 * Azinphos-ethyl 2642-71-9 ESI + M+H+ 346,0 26 132,2 21 160,2 15 0,96 * Azinphos-methyl 86-50-0 ESI + M+H+ 318,0 16 132,2 21 160,2 13 0,89 * Azocyclotin 41083-11-8 ESI + M-OH+ 369,2 76 204,8 23 287,0 17 n.a. n.a. Azoxystrobin 131860-33-8 ESI + M+H+ 404,1 36 371,9 19 3