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Research ArticleAnalysis of Veterinary Drug and Pesticide Residues Usingthe Ethyl Acetate Multiclass/Multiresidue Method in Milk byLiquid Chromatography-Tandem Mass Spectrometry
Husniye Imamoglu1 and Elmas Oktem Olgun2
1 Istanbul Sabahattin Zaim University, Halkalı, 34303 Istanbul, Turkey2TUBITAK Marmara Research Centre, Food Institute, P.O. Box 21, Gebze, 41470 Kocaeli, Turkey
Correspondence should be addressed to Husniye Imamoglu; [email protected]
Received 11 February 2016; Accepted 12 April 2016
Academic Editor: Jose M. M. Lopez
Copyright © 2016 H. Imamoglu and E. Oktem Olgun. This is an open access article distributed under the Creative CommonsAttribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work isproperly cited.
A rapid and simple multiclass, ethyl acetate (EtOAc) multiresidue method based on liquid chromatography coupled with tandemmass spectrometry (LC-MS/MS) detection was developed for the determination and quantification of 26 veterinary drugs and 187total pesticide residues in milk. Sample preparation was a simple procedure based on liquid–liquid extraction with ethyl acetatecontaining 0.1% acetic acid, followed by centrifugation and evaporation of the supernatant. The residue was dissolved in ethylacetate with 0.1% acetic acid and centrifuged prior to LC-MS/MS analysis. Chromatographic separation of analytes was performedon an Inertsil X-Terra C18 columnwith acetic acid inmethanol andwater gradient.The repeatability and reproducibility were in therange of 2 to 13% and 6 to 16%, respectively. The average recoveries ranged from 75 to 120% with the RSD (𝑛 = 18). The developedmethod was validated according to the criteria set in Commission Decision 2002/657/EC and SANTE/11945/2015. The validatedmethodology represents a fast and cheap alternative for the simultaneous analysis of veterinary drug and pesticide residues whichcan be easily extended to other compounds and matrices.
1. Introduction
Veterinary drugs are widely used in medical and veterinarypractices to treat and prevent disease as well as improve feedefficiency and increase animal growth rates [1]. Pesticides arealso widely used to enhance food production by protectingfood crops frompotentially harmful and destructive pests [2].However, the resulting occurrence of contaminants and/orresidues in the human diet represents an issue of highconcern.
According to the European Union, the maximum residuelimit (MRL) in dairy milk is 100𝜇g/kg for tetracycline andsulfenamide, 50𝜇g/kg for macrolides and quinolones, and10 𝜇g/kg for pesticides. Sensitive analytic methods have beendeveloped to monitor and detect the MRL values in thedairy milk [3]. There are ultra-high pressure liquid chro-matography mass spectrometry (UHPLC-MS/MS) methods
reported to detectmultiple residues of𝛽-lactams [4, 5], aswellas pesticides and mycotoxins [6], and some antihelminthicdrugs and phenylbutazone [7].
Milk is a complex food that is high in fat and protein,and such ingredients may cause interactions in the ana-lytical processes. Therefore, sample preparation is required,particularly in extraction and cleanup. Formerly, samplepreparation methods were based on a few compounds ora single class of such drugs. Applying common extractionprocedures and developing chromatographic conditions aredifficult in multiclass and multiresidue analyses. Solid phaseextraction methods have been applied, after the phases ofprotein precipitation and centrifugation, in order to observethe fluoroquinolones [8], veterinary drugs [9], mycotoxins,and pesticides in milk [6, 10]. However, these methods aregenerally found to be time-consuming and require largevolumes of organic solvents.
Hindawi Publishing CorporationJournal of Analytical Methods in ChemistryVolume 2016, Article ID 2170165, 17 pageshttp://dx.doi.org/10.1155/2016/2170165
2 Journal of Analytical Methods in Chemistry
Multiresidue veterinary drugs that were developed formilk tests depend on various extraction and cleanup prin-ciples. One of the most accepted approaches is to dilute asample of milk with a solvent like acetonitrile and then tocentrifuge and evaporate the obtained supernatant organicextract [11, 12]. Some multiclass analytical method applica-tions by LC-MS/MS or LC-TOF/MS, related to homogenizedor raw milk, that have the ability to specify undesirablechemicals, such as tetracycline, quinolone, sulfonamide, pep-tide, hormone, nonsteroidal anti-inflammatory anthelminticdrugs, mycotoxin, and pesticides, can be found in theliterature [7]. Yet most of these methods are unable tooffer satisfactory recovery of a large range of compounds ofdifferent polarities [13, 14].
Most methods for the analysis of veterinary residues havesome disadvantages, including high solvent consumption,tedious SPE cleanup steps that require extended time foranalysis, and high costs. Therefore, these types of methodsare not applied for routine analyses. The Quick Easy CheapEffective Rugged Safe (QuEChERS) methodology, whichwas originally developed for pesticide analysis, has recentlybeen proposed for the analysis of veterinary drugs usingdifferent matrices [15–18]. However, QuEChERS was foundto be inconvenient for the recovery of polar veterinarydrugs, including penicillin, tetracycline, and quinolone [13,18, 19]. Therefore, there is still a great need for simpleand rapid multiresidue analytical methods for simultane-ously determining veterinary drug and pesticide residues inmilk.
In this study, we prepared milk samples by using aprocedure based on a simple liquid-to-liquid extraction.Thismethod utilized a simple and quick sample preparation pro-cedure using a single extraction step. Through this method,milk samples were analyzed for the determination of bothveterinary drugs and pesticide residues by utilizing liquidchromatography-tandem mass spectrometry (LC-MS/MS).As a result, the reduced use of chemicals and steps in thesample preparation phase, together with the avoidance of asample cleanup step, simplified the sample pretreatment andreduced the overall total cost. Finally, in addition to reducinganalyses costs, the method provided a higher recovery ofcompounds of various polarities and improved the simplicityof detection efforts.
2. Materials and Methods
2.1. Reagents and Chemicals. HPLC grade acetonitrile(ACN), methanol, ethyl acetate (EtOAc) (Lichrosolv, purity≥ 99.9), and glacial acetic acid (Emprove, 100%) werepurchased from Merck (Darmstadt, Germany). The waterused to prepare the solutions was purified in a Milli-QPlus system (EMD Millipore, Billerica, MA). Magnesiumsulfate, sodium chloride, Supelclean� primary secondaryamine (PSA), pure tetracyclines, sulfonamides, quinolones,macrolides, and antibiotics were provided from SigmaAldrich (St. Louis, Missouri, USA) and the pesticides wereprovided from Dr. Ehrenstrorfer (Augsburg, Germany).
2.2. Samples. All pasteurized whole milk samples were pur-chased from local markets. Also, raw milk was used forinterference and specificity/selectivity as a blank.
Standard Solutions. Individual stock solutions of the veteri-nary drugs and pesticides were prepared in acetonitrile at aconcentration of 1000mg/kg. Amixed intermediate standardsolutionwas prepared by diluting the stock standard solutionsof the veterinary drugs and pesticides in acetonitrile at aconcentration of 10mg/kg. Stock and intermediate standardsolutions were stored at 4∘C in amber flasks and were foundstable for at least 6 months.
2.3. Extraction Procedures
2.3.1. Ethyl Acetate Extraction without Salting Procedure.Milk samples, upon arrival at our laboratory, were kept atrefrigerator temperature (10 ± 4∘C) until analysis. For thepreparation an aliquot of approximately 5mL milk samplewas pipetted in a 50mL polypropylene centrifuge tube.Then,200mcL acetic acid was added to 10mL of ethyl acetate.After vortex for 3 minutes, the mixture was centrifuged at5000 rpm for 10 minutes. The upper phase was taken in15mL centrifuge tube and was dried under a gentle streamof nitrogen, and the residue was reconstituted with 1000mcLof mobile phase A/mobile phase B (80/20). The sample wasvortexed vigorously for 10 minutes. The extract was filteredthrough a 0.45 𝜇m filter prior to LC-MS/MS analysis.
2.3.2. Acetonitrile Extraction without Salting Procedure.Approximately 5mL milk sample was pipetted in a 50mLpolypropylene centrifuge tube. Then, 10mL of acetonitrileand 200mcL acetic acid were added to milk. After mixing bya vortex stirrer for 3 minutes, the mixture was centrifugedat 5000 rpm for 10 minutes. The upper phase was taken in15mL centrifuge tube and was dried under a gentle streamof nitrogen, and the residue was reconstituted with 1000mcLof mobile phase A/mobile phase B (80/20). The sample wasvortexed vigorously for 10 minutes. The extract was filteredthrough a 0.45 𝜇m filter prior to LC-MS/MS analysis.
2.3.3. QuEChERS Extraction Procedure. Approximately 5mLmilk sample was pipetted in a 50mL polypropylene cen-trifuge tube. Then, 2 g of magnesium sulfate and 1 g ofsodium acetate were added to milk samples [15]. Then,10mL of acetonitrile and 100mcL acetic acid were added tomilk samples. After vortex for 3 minutes, the mixture wascentrifuged at 5000 rpm for 10 minutes. The upper phasewas taken in 15mL centrifuge tube and was dried under agentle stream of nitrogen, and the residue was reconstitutedwith 1000mcL of mobile phase A/mobile phase B (80/20).The extract was transferred to a 2mL Eppendorf microtubecontaining 50mg PSA and 200mg magnesium sulfate. Then,the tube was centrifuged at 4000 rpm during 5 minutes. Theextract was filtered through a 0.45 𝜇m filter prior to LC-MS/MS analysis.
2.4. LC-MS/MS Analysis. The chromatographic analyseswere performed using an HPLC system consisting of a
Journal of Analytical Methods in Chemistry 3
020406080
100120140
Reco
very
(%)
QuEChERSACN without saltEtOAc without salt
Acrin
athr
inBu
toca
rbox
im su
lfoxi
deCa
dusa
fos
Des
med
ipha
mEp
oxic
onaz
ole
Fost
hiaz
ate
Hep
teno
phos
Lufe
nuro
nO
met
hoat
ePi
colin
afen
Qui
zalo
fop-
P-et
hyl
Rim
sulfu
ron
Sim
azin
eTr
itico
nazo
leVa
mid
othi
onCh
lort
etra
cycli
neD
anofl
oxac
inFl
umeq
uine
Josa
myc
inLo
mefl
oxac
inO
rbifl
oxac
inRi
fam
pici
nSa
raflo
xaci
nSu
lfach
loro
pyrid
azin
eTi
lmic
osin
Tetr
acyc
line
Isox
aben
Figure 1: Recovery data for three different extraction procedures.
binary pump (Shimadzu UFLC LC-20ADmodel), Shimadzuautomatic injector (Autosampler SIL-20A HT model), and acolumn oven (CTO-20AC). Analytical columns, Symmetry�C18 2.1× 150mm id, 5 𝜇mparticle size (Waters,Milford,MA),andWaters XTerraC18 150mm× 2.1mm id, 5 𝜇mparticle size(Waters, Milford, MA), were tested. Chromatographic sepa-ration of veterinary drugs and pesticides was carried out on aWaters Symmetry C18 column. The method used a gradientmobile phase containing 0.1% acetic acid water and mobilephase B containing methanol. The column temperature wasmaintained at 40∘C with a flow rate of 0.3mL/min. The gra-dient profilewas scheduled as follows: initial proportion (98%A and 2% B) for 0.3 minutes, linear increase to 80% (B) until7 minutes, and hold of 80% (B) for 3 minutes. The injectionvolume was 50 𝜇L.The chromatographic system was coupledto electrospray ionization (ESI) source followed by anAppliedBiosystems MDS SCIEX 4500 Q TRAP mass spectrometer.The MS/MS detector conditions were as follows: curtain gas20mL/min, exit potential 10V, ion source gas 1 and ion sourcegas 2 set at 50mL/min, ion spray voltage 5500V, and turbospray temperature set at 550∘C. MS data were acquired inthe positive ion ESI mode using two alternating MS/MS scanevents. Two transitions were monitored for each analyte. Theselected molecular ion and optimized collision voltages ofproduct ions used for quantification, confirmation, and ionratio were summarized in Table 1. Applied Biosystems SCIEXAnalyst software version 1.6 was employed for data acquisi-tion and processing.Quantificationwas by comparisonwith asix-point calibration (0.0, 0.01, 0.025, 0.05, 0.1, and 0.2mg/kg)in matrix-matched calibration.
2.5. Validation Study. The analytical method developed fordetermination of veterinary drug and pesticide residues inmilk was validated according to EU Decision 2002/657/EC[16] and SANTE/11945/2015 [17]. The following parameterswere evaluated in the validation procedure: selectivity, sensi-tivity, linearity, precision (intraday and interday reproducibil-ity), accuracy and CC𝛼 and CC𝛽, LOD, and LOQ.
3. Results and Discussion
3.1. Optimization of the Extraction Procedures. Ethyl acetateextraction without salt procedure was chosen to be per-formed in this study because of its advantages. There was noneed to use salt and it could give lower detection limit interms of volatile characteristic of ethyl acetate.
Recovery values showedno difference among three differ-ent extraction procedures (acetonitrile extraction, QuECh-ERS extraction, and ethyl acetate extraction without saltingprocedure) (Figure 1).
The recovery values expressed as recovery % are allwithin the reference range of 70–120%. Comparing threeprocedures, EtOAc without salt provided recoveries between100% and 120% for a higher number of veterinary drugs andpesticides (26 veterinary drugs and 134 pesticides; total of160 compounds) thanQuEChERS (82 compounds) andACN(100 compounds), as it can be observed in Figure 2. In termsof extraction recoveries, EtOAc was found to be a suitableextraction procedure for all 26 veterinary drugs and mostof the pesticides analyzed in this study. Only one analyte(propham) showed 𝑅 > 120 for EtOAc.
Accuracywas evaluated in terms of relative standard devi-ation (RSD) by spiking blank samples with the correspondingvolume of the multicompound working standard solution.RSD was evaluated at 50 𝜇g/kg by spiking six blank samplesat each level for three procedures that provided similar RSDvalues. These values were within 1 < RSD < 10 for 75% ofeach analyte in the three procedures. These results indicatedthat the EtOAcwithout saltmethodwas precise, accurate, andreliable for the analysis of the veterinary drug and pesticidecompounds in the milk samples as an alternative method.
3.2. LC-MS/MS. Mobile phase was acidified with acetic acidin methanol and water. Also, study [18] in the literature wasperformed for the comparison. Formic acid in acetonitrileand water was used as a mobile phase in [18]. According toanalyte intensities, our results gave better peak shapes than
4 Journal of Analytical Methods in Chemistry
Table 1: LC-MS/MS ion parameters.
Compounds Precursor ion Transition 1 Transition 2 Ion ratio(𝑚/𝑧) (𝑚/𝑧) (𝑚/𝑧) (%)
2,4-D (negative) 219 160 125 952,4,5-T 253 195 197 982,4-Dimethylaniline 122 107 80Acetamiprid 223 126 73 22Acrinathrin 560 208 181 75Alachlor 238 162 238 12Amitraz 294 163 122 75Atrazine 216 174 104 45Azoxystrobin 404 372 344 33Bentazon (−)239 132 197 78Bifenazate (−)300 253 239 79Bitertanol 339 70 269 81Boscalid 344 307 140 61Bromacil (−)259 205 203 55Bromuconazole 378 159 70 66Bromoxynil (−)274 79 81 67Bupirimate 317 108 166 86Buprofezin 307 116 201 93Butocarboxim sulfoxide 207 75 132 88Cadusafos 272 159 97 98Carbaryl 202 145 127 34Carbendazim 192 160 132 17Carbofuran 222 165 123 98Carbosulfan 381 118 160 90Carboxin 234 143 87 85Dimethoate 230 199 125 97Dimethomorph 388 301 165 58Dimoxystrobin 328 116 205 99Diniconazole 326 70 159 65Dinobuton 327 215 152 66Dinocap (sum) 295 193 209 89Dinoterb (−)239 207 176 85Diphenylamine 171 93 152 17Disulfoton-sulfoxide 291 185 213 87Dithianon (−)296 263 238 86Diuron 233 72 160 85Epoxiconazole 330 121 101 80EPTC 191 128 86 40Ethiofencarb 226 107 164 81Ethion 402 385 199 76Ethirimol 211 98 140 87Ethofumesate 304 121 161 25Etoxazole 361 141 113 86Ethoxyquin 219 160 174 84Famoxadone 392 238 331 84Fenamidone 313 92 236 83Fenamiphos 304 217 202 59Fenarimol 331 268 81 18Fenazaquin 307 161 147 80
Journal of Analytical Methods in Chemistry 5
Table 1: Continued.
Compounds Precursor ion Transition 1 Transition 2 Ion ratio(𝑚/𝑧) (𝑚/𝑧) (𝑚/𝑧) (%)
Fenbuconazole 338 70 125 88Fenhexamid 303 97 55 63Fenitrothion 278 125 109 60Fenoxycarb 302 88 116 25Fenpropathrin 367 125 350 33MCPP (−)213 141 143 18Metalaxyl-M 280 160 220 85Mepanipyrim 225 106 77 17Mesosulfuron-methyl 505 182 83 15Metazachlor 279 210 134 82S-Metolachlor 284 252 254 81Metosulam 419 175 140 94Metribuzin 215 187 84 29Monocrotophos 224 127 98 9Monolinuron 216 126 148 43Monuron 199 72 126 76Omethoate 215 125 125 10Oxadiargyl 341 223 151 87Oxadiazon 363 220 177 88Oxadixyl 280 219 133 79Oxamyl 237 72 90 65Oxasulfuron 408 150 107 89Oxycarboxin 269 175 147 31Oxyfluorfen 362 316 237 27Penconazole 284 70 159 67Pendimethalin 282 212 194 19Pethoxamid 297 131 250 62Phosalone 368 182 111 31Phenmedipham 301 136 168 54Phenthoate 321 163 79 18Phosmet 318 160 133 13Phosphamidon 300 127 174 28Picloram (−)239 196 123 56Terbuthylazine 230 174 104 55Pirimicarb 239 72 93Thiacloprid 254 126 186 18Thiamethoxam 292 211 181 39Thifensulfuron-methyl 389 167 205 14Thiodicarb 355 88 108 22Thiophanate-methyl 343 151 192 34Triadimefon 294 197 225 30Triadimenol 296 227 70 9Triallate 304 86 143 67Triasulfuron 403 167 141 67Triazophos 314 119 162 54Tribenuron-methyl 397 155 181 66Tributylphosphate 268 98 67
6 Journal of Analytical Methods in Chemistry
Table 1: Continued.
Compounds Precursor ion Transition 1 Transition 2 Ion ratio(𝑚/𝑧) (𝑚/𝑧) (𝑚/𝑧) (%)
Trichlorfon 274 109 221 75Tridemorph 298 130 116 84Trifloxystrobin 410 186 206 37Triflumizole 346 73 278 26Triticonazole 318 70 125 95Vamidothion 288 146 118 33Zoxamide 336 159 189 26Ciprofloxacin 332 314 288 82Clindamycin 425 126 82 97Chlortetracycline 479 462 444 88Danofloxacin 360 316 342 88Difloxacin 400 356 299 90Doxycycline hydrate 445 428 410 97Flumequine 860 174 109 56Josamycin 828 109 174 75Clofentezine 303 138 102 88Chloridazon 223 104 92 54Chlorfenvinphos 359 155 99 51Chlorfluazuron (−)538 518 355 88Chloroxuron 292 72 218 87Chlorpyrifos 350 198 200 8Chlorsulfuron 359 141 167 89Chlorthiamid 206 189 154 25Cinidon-ethyl 412 348 107 26Cyazofamid 326 108 261 35Cyclanilide (−)272 160 228 45Cycloate 216 154 134 48Cymoxanil 199 128 111 59Cyproconazole 292 70 125 65Cyprodinil 226 93 77 80Demeton-S-methyl 231 89 61 62Demeton-S-methylsulfoxide 247 109 169 26Desmedipham 318 182 136 88Diallate 271 86 109 36Diazinon 305 169 97 62Dichlofluanid 350 123 224 16Dichlorprop (−)233 161 125 87Dichlorvos 221 109 127 15Difenoconazole 406 251 337 32Dimethenamid (sum) 277 244 168 68Fenthion 279 169 247 33Flazasulfuron 409 182 227 46Fludioxonil (−)247 126 169 57Fluazifop-P-butyl 385 282 328 62Flufenacet 365 194 152 61Flufenoxuron (−)488 156 304 99Flurochloridone 313 292 145 48Flurtamone 335 178 247 79
Journal of Analytical Methods in Chemistry 7
Table 1: Continued.
Compounds Precursor ion Transition 1 Transition 2 Ion ratio(𝑚/𝑧) (𝑚/𝑧) (𝑚/𝑧) (%)
Flusilazole 317 165 247 78Flutolanil 325 262 242 45Foramsulfuron 454 182 139 54Fosthiazate 285 104 228 55Furathiocarb 384 195 252 62Heptenophos 251 127 109 9Hexythiazox 353 228 168 81Imazalil 297 159 201 88Imazamox (−)304 259 217 10Imazaquin 313 199 128 25Imazosulfuron 413 156 260 38Imidacloprid 256 209 175 84Indoxacarb 529 203 56 84Ioxynil (−)370 127 243 99Iprovalicarb 322 119 203 95Isazofos 314 120 162 34Isoproturon 208 72 165 99Isoxaben 334 165 150 48Lufenuron (−)509 326 339 46Malathion 331 127 99 86MCPA (−)199 141 155 94Picolinafen 378 238 145 57Mecarbam 331 227 97 96Pirimiphos-methyl 306 108 164 68Prochloraz 376 308 266 33Profenofos 373 303 97 60Prometryn 242 158 68 68Propamocarb 190 102 144 39Propanil 218 162 127 66Propargite 368 175 231 65Propham 180 138 120 28Propiconazole 342 159 69 62Propyzamide 256 190 173 63Pymetrozine 219 105 79 11Pyraclostrobin 389 194 163 98Pyridaben 365 309 147 78Pyridaphenthion 341 205 189 88Pyridate 380 207 351 78Pyriproxyfen 322 96 185 62Quinalphos 300 147 163 54Quinoxyfen 309 197 162 97Quizalofop-P-ethyl 374 299 56Rimsulfuron 433 182 325 55Simazine 202 124 132 70Spiroxamine 299 144 100 87Sulfosulfuron 472 211 261 89Tebuconazole 308 70 125 55
8 Journal of Analytical Methods in Chemistry
Table 1: Continued.
Compounds Precursor ion Transition 1 Transition 2 Ion ratio(𝑚/𝑧) (𝑚/𝑧) (𝑚/𝑧) (%)
TEPP 291 179 99 96Terbutryn 242 186 68 51Tetrachlorvinphos 367 127 241 95Thiabendazole 203 175 131 12Oxytetracycline 461 426 443 97Rifampicin 823 791 151 91Sarafloxacin 386 368 342 92Sulfachloropyridazine 285 156 207 75Sulfaquinoxaline 301 156 108 99Sulfadiazine 251 156 92 86Sulfamerazine 265 156 108 89Sulfathiazole 256 156 92 88Sulfamethazine 279 186 124 99Sulfadoxine 311 156 108 97Sulfapyridine 250 184 156 96Sulfaclozine 285 156 108 95Sulfamethoxazole 254 92 108 99Tilmicosin 869 522 678 97Tetracycline 445 428 410 85Lomefloxacin 407 126 82 88Orbifloxacin 396 352 295 88Oxolinic acid 262 244 202 89
0
20
40
60
80
100
120
140
160
180
100 < R < 120 R > 120
Num
ber o
f ana
lyte
s
Recoveries (%)
QuEChERSACN
EtOAc without salt
70 < R < 100
Figure 2: Recovery (%) data obtained using extraction procedures;QuEChERS, ACN, and EtOAc without salt.
chromatograms in [18].The dried residuewas redissolved in amixture ofMeOH/water with 0.1% acetic acid to test differentreconstitution solvents. This composition produced betterpeak shapes for all analytes compared with water-methanol
(80 : 20) that gave lower response. Increasing acetic acid to 1%in the mixture did not improve chromatography but causedextra peaks in the background noise.
3.3. Validation Study
3.3.1. Selectivity. The selectivity of the method was assessedby duplicate analysis of 10 blank milk samples. No peaks ofinterfering compounds were observed within the intervals ofthe retention time of the analytes in any of these samples.
3.3.2. Linearity. Linearity was evaluated from the calibrationcurves by triplicate analyses of blank milk samples fortifiedwith the analytes at six (0.0, 0.01, 0.025, 0.05, 0.1, and0.2mg/kg) concentration levels. Linearity was expressed asthe coefficient of linear correlation (𝑟) and from the slope ofthe calibration curve. The linearity of the analytical responseacross the studied range was excellent, with correlation coef-ficients higher than 0.997 for all analytes, which was similarto the findings in [19]. The authors [20] found correlationcoefficients higher than 0.992 for all analytes, which was alower score than ours.
3.3.3. Decision Limit and Detection Capability. CC𝛼 isdefined as the limit at and above which it can be concludedwith an error probability of 𝛼 that a sample is noncompliant.CC𝛽 is defined as the smallest content of the substance thatmay be detected, identified, and/or quantified in a samplewith an error probability of 𝛽. The CC𝛼 and CC𝛽 were
Journal of Analytical Methods in Chemistry 9
0.0
15.50
15.71
15.96
15.61
5.0e4
0.0
3.3e4
0.0
3.0e5
0.0
1.5e4
1.0e4
1.0e51.4e5
555045403530252015105
555045403530252015105
555045403530252015105
555045403530252015105
Time (min)
Time (min)
Time (min)
Time (min)
XIC of +MRM (40 pairs): 445.302/410.200 Da ID: tetracycline from sample 3(std) of 2201 vet.wiff (turbo spray)
XIC of +MRM (40 pairs): 311.104/156.100 Da ID: sulfadimethoxine from sample 3(std) of 2201 vet.wiff (turbo spray)
XIC of +MRM (40 pairs): 461.172/426.000Da ID: oxytetracycline from sample 3(std) of 2201 vet.wiff (turbo spray)
XIC of +MRM (40 pairs): 251.124/156.000 Da ID: sulfadiazine from sample 3(std) of 2201 vet.wiff (turbo spray)
Max. 3.0e5 cps.
Max. 1.5e4 cps.
Max. 3.3e4 cps.
Max. 1.4e5 cps.
Figure 3: MRM chromatograms of milk samples at the LOQ level of tetracyclines, sulfadimethoxine, oxytetracycline, and sulfadiazine(10𝜇g/kg).
determined by analysis of 10 blank milk samples and thesignal-to-noise (S/N) ratio is calculated at the timewindow inwhich the analyte is expected.TheCC𝛼 valueswere calculatedas three times the S/N ratio. The CC𝛽 was calculated byanalyzing 10 blank samples spiked with concentration atCC𝛼. Then the CC𝛼 value was added up to 1.64 timesthe corresponding standard deviation. Then, a preliminaryexperiment was conducted to check if all compounds weredetected when spiked at their CC𝛼 level (Table 2).
In Figure 3, very satisfactory S/N ratios were obtainedfor all analytes at LOQ level. The lowest LOQ value was50 𝜇g/kg for tetracyclines and for sulfonamides 20𝜇g/kg inveterinary drugs in [20] while it was 10 𝜇g/kg for both of themin our study except ciprofloxacin and quinolone. Figure 3shows MRM chromatograms of milk samples at the lowestvalidation concentration at LOQ level.
3.3.4. Accuracy and Precision. The accuracy was evaluated byrecovery tests, analyzing fortified blank samples at the sameconcentration levels used in the precision tests (0.01, 0.025,and 0.05mg/kg). The accuracy and precision of the method
results (Table 2) confirmed the values given in Decision2002/657/EC [16]. Thus, the mean accuracy values obtainedin the recovery tests were between 61 and 130%.The precisionof the method was determined in two stages: repeatability(intraday) and intermediate precision (interday). Repeatabil-ity was expressed by the RSD of the results from six replicatesanalyzed on the same day by the same analyst using thesame instrument. The intermediate precision was expressedby the RSD of the results of eighteen analyses performed onthree different days (𝑛 = 3), six analyses/day, by the sameanalyst using the same instrument. The relative standarddeviation (RSD) of interday values of veterinary drugs andpesticides analyzed by the present method was 2 to 13% andfor the intraday test 5–19% (Table 2), while relative standarddeviation (RSDr) of intraday values was 4–26% in [20].
3.3.5. Matrix Effects. Evaluation of matrix effect is importantduring validation of analytical methods using the LC-MS/MStechnique. The ionization efficiency of the analytes in ESIsource may be affected by matrix interference. In order toevaluate the degree of ion suppression or signal enhancement,
10 Journal of Analytical Methods in Chemistry
Table2:Va
lidationresults
ofthed
evelop
edmetho
d.
Com
poun
ds𝑟2
LOQ
MRL
CC𝛼
CC𝛽
%recovery
%RS
D%recovery
%RS
D%recovery
%RS
D%RS
Dr
Relativ
eMatrix
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
10(𝜇g/kg)
10(𝜇g/kg)
25(𝜇g/kg)
25(𝜇g/kg)
50(𝜇g/kg)
50(𝜇g/kg)
uncertainty%
effect
2,4-D(negative)
0.997
1110
2133
112
890
6108
513
320.81
2,4,5-T
0.998
910
1826
8518
102
1793
911
230.92
2,4-Dim
ethylanilin
e0.998
810
1826
7911
110
897
811
350.99
Acetam
iprid
0.997
1010
1826
979
102
896
711
330.92
Acrin
athrin
0.998
1110
1826
106
1088
8104
711
350.81
Alachlor
0.997
1110
2030
108
1186
492
313
280.81
Amitraz
0.997
910
2030
868
764
763
1428
0.81
Atrazine
0.997
1110
1723
109
694
591
39
300.85
Azoxystrobin
0.998
1110
2133
1149
102
5110
414
300.92
Bentazon
0.998
1210
1723
1185
944
944
828
0.85
Bifenazate
0.998
1110
2030
109
10102
7111
611
330.92
Bitertanol
0.998
1110
1723
112
598
397
38
260.88
Boscalid
0.998
1210
1520
115
6110
6101
57
300.99
Brom
acil
0.998
910
2030
9116
108
1491
1113
420.97
Brom
ucon
azole
0.997
1110
2030
109
9100
895
614
300.90
Brom
oxyn
il0.997
1010
1723
9914
106
999
69
330.96
Bupirim
ate
0.997
1210
2030
116
5100
5104
312
260.90
Buprofezin
0.997
910
1723
9016
9012
888
1026
0.81
Butocarboxim
sulfo
xide
0.997
1110
1723
107
9118
8102
77
331.0
6Ca
dusafos
0.997
1110
1520
11011
948
955
630
0.85
Carbaryl
0.997
1110
1723
105
1094
589
49
280.85
Carbendazim
0.997
1210
2030
118
5122
5113
411
301.10
Carbofuran
0.998
1210
1723
116
490
492
38
260.81
Carbosulfan
0.997
910
2133
9110
106
693
615
320.96
Carboxin
0.998
1110
1826
1136
904
895
1228
0.81
Clofentezine
0.998
910
1723
8813
9810
938
1026
0.88
Chlorid
azon
0.998
1010
1826
102
11114
997
711
301.0
3Ch
lorfe
nvinph
os0.998
1110
1826
112
896
5100
310
300.86
Chlorfluazuron
0.998
1110
2133
107
10114
5108
614
301.0
3Ch
loroxu
ron
0.997
1110
1826
108
13102
5104
510
360.92
Chlorpyrifo
s0.997
1110
1723
108
9102
6107
67
320.92
Chlorsulfuron
0.997
1010
2133
9610
925
885
1530
0.83
Chlorthiam
id0.997
910
2133
9217
104
13114
913
320.94
Journal of Analytical Methods in Chemistry 11
Table2:Con
tinued.
Com
poun
ds𝑟2
LOQ
MRL
CC𝛼
CC𝛽
%recovery
%RS
D%recovery
%RS
D%recovery
%RS
D%RS
Dr
Relativ
eMatrix
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
10(𝜇g/kg)
10(𝜇g/kg)
25(𝜇g/kg)
25(𝜇g/kg)
50(𝜇g/kg)
50(𝜇g/kg)
uncertainty%
effect
Cinido
n-ethyl
0.997
1110
1723
105
7100
6110
58
320.90
Cyazofam
id0.997
1110
1826
1127
947
934
1028
0.85
Cycla
nilid
e0.997
1210
2133
115
5104
5113
513
300.94
Cyclo
ate
0.998
1110
1723
106
1296
1188
59
280.86
Cymoxanil
0.998
1110
1723
109
7112
6103
68
321.0
1Cy
procon
azole
0.998
1010
1826
9610
926
984
1228
0.83
Cyprod
inil
0.998
910
2030
9116
989
110
911
300.88
Dem
eton
-S-m
ethyl
0.998
1010
2030
9616
9811
101
411
280.88
Dem
eton
-S-m
ethylsu
lfoxide
0.998
1010
1317
100
8101
799
611
350.91
Desmedipham
0.998
1010
1317
998
988
877
140
0.88
Diallate
0.998
1010
2030
100
13120
12110
614
261.0
8Diazino
n0.998
1010
1213
959
926
100
512
320.83
Dichlofl
uanid
0.998
1010
1723
103
9104
8100
812
260.94
Dichlorprop
0.998
910
1826
885
884
953
80
0.82
Dichlorvos
0.998
910
1520
9314
118
11109
1116
351.0
6Difeno
conazole
0.998
910
1520
9212
100
994
411
280.90
Dim
ethenamid
(sum
)0.998
1110
1723
11213
989
8710
1028
0.94
Dim
etho
ate
0.998
1110
1723
1138
104
7100
69
260.94
Dim
etho
morph
0.998
910
1317
9112
104
897
514
280.94
Dim
oxystro
bin
0.998
1010
1520
101
8116
597
512
301.0
5Dinicon
azole
0.998
1010
1317
9719
9615
879
1036
0.86
Dinob
uton
0.998
1010
1723
104
1078
692
611
320.82
Dinocap
(sum
)0.998
1210
1317
115
796
590
414
300.86
Dinoterb
0.997
1210
1826
1157
100
498
49
280.90
Diphenylamine
0.999
1210
1317
115
7108
590
414
300.97
Disu
lfoton-sulfo
xide
0.997
1110
1317
109
1086
694
513
300.82
Dith
iano
n0.997
1110
1317
106
6108
5102
36
260.97
Diuron
0.999
1110
2030
109
994
7101
310
260.85
Epoxicon
azole
0.997
1110
1213
105
898
493
411
280.88
EPTC
0.997
1110
1826
113
7112
496
410
281.0
1Ethiofencarb
0.997
1210
1826
115
796
596
39
260.86
Ethion
0.998
1010
1520
102
10100
898
812
220.90
Ethirim
ol0.998
1010
1520
9815
969
111
813
330.86
Etho
fumesate
0.998
1110
1723
105
1196
10100
713
280.86
Etoxazole
0.998
1110
1723
1148
945
101
411
280.85
12 Journal of Analytical Methods in Chemistry
Table2:Con
tinued.
Com
poun
ds𝑟2
LOQ
MRL
CC𝛼
CC𝛽
%recovery
%RS
D%recovery
%RS
D%recovery
%RS
D%RS
Dr
Relativ
eMatrix
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
10(𝜇g/kg)
10(𝜇g/kg)
25(𝜇g/kg)
25(𝜇g/kg)
50(𝜇g/kg)
50(𝜇g/kg)
uncertainty%
effect
Etho
xyqu
in0.998
1010
1317
100
1396
1198
411
300.86
Famoxadon
e0.998
1110
1520
112
12114
5117
512
321.0
3Fenamidon
e0.998
1110
1317
108
984
891
610
260.82
Fenamipho
s0.998
1110
1723
107
5106
4109
35
320.96
Fenarim
ol0.998
1010
1317
101
1199
995
811
230.89
Fenazaqu
in0.997
1110
1826
1138
128
7113
810
281.15
Fenb
ucon
azole
0.997
910
1317
8616
9412
974
832
0.85
Fenh
exam
id0.997
1110
1826
1147
806
845
1328
0.82
Fenitro
thion
0.997
1010
1723
9912
9811
949
1124
0.88
Feno
xycarb
0.997
910
1317
8516
100
14103
89
350.90
Fenp
ropathrin
0.997
1010
1826
100
12100
1099
97
250.90
Fenthion
0.997
1010
2336
9512
11211
108
712
331.0
1Flazasulfuron
0.998
1010
3049
9510
1188
1167
1530
1.06
Flud
ioxonil
0.998
1210
2336
115
788
5100
513
250.82
Fluazifop-P-bu
tyl0.998
1210
2846
118
8102
696
511
320.92
Flufenacet
0.998
1010
2540
103
1096
9100
713
280.86
Flufenoxuron
0.998
1010
2643
958
100
8105
411
320.90
Flurochloridon
e0.998
1010
1826
100
10102
9112
67
280.92
Flurtamon
e0.998
1010
2030
103
690
489
410
320.81
Flusilazole
0.998
1010
2336
104
892
699
611
320.83
Flutolanil
0.998
1210
1826
115
6114
799
710
261.0
3Fo
ramsulfu
ron
0.998
1110
2540
105
486
399
414
260.82
Fosthiazate
0.997
810
2030
8213
945
943
1330
0.85
Furathiocarb
0.997
1210
2133
115
596
590
512
330.86
Hepteno
phos
0.997
1010
3153
9915
9412
907
1128
0.85
Hexythiazox
0.997
1010
2540
103
6100
498
59
320.90
Imazalil
0.997
1010
2846
9512
100
1188
109
280.90
Imazam
ox0.997
810
1826
8411
100
992
612
260.90
Imazaquin
0.997
1110
3153
112
990
586
312
00.81
Imazosulfuron
0.997
1010
2540
9812
9511
968
1136
0.86
Imidacloprid
0.999
910
3049
8712
102
9109
615
260.92
Indo
xacarb
0.999
1010
2336
9915
100
693
816
300.90
Ioxynil
0.999
1010
2030
994
844
815
830
0.81
Iprovalicarb
0.999
1010
2030
9712
1108
104
715
320.99
Isazofos
0.999
1210
2133
115
794
589
1113
260.85
Isop
roturon
0.999
1210
2030
115
890
697
611
380.81
Isoxaben
0.997
1110
2643
112
5110
396
58
300.99
Lufenu
ron
0.997
1010
2643
994
984
944
1330
0.88
Malathion
0.999
1210
2336
115
7104
589
613
330.94
Journal of Analytical Methods in Chemistry 13
Table2:Con
tinued.
Com
poun
ds𝑟2
LOQ
MRL
CC𝛼
CC𝛽
%recovery
%RS
D%recovery
%RS
D%recovery
%RS
D%RS
Dr
Relativ
eMatrix
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
10(𝜇g/kg)
10(𝜇g/kg)
25(𝜇g/kg)
25(𝜇g/kg)
50(𝜇g/kg)
50(𝜇g/kg)
uncertainty%
effect
MCP
A0.997
910
2540
939
102
5103
711
280.92
Mecarbam
0.998
1110
3153
105
16106
1494
711
300.96
MCP
P0.998
1010
2846
103
1284
997
912
410.82
Metalaxyl-M
0.998
1010
2336
977
122
4101
516
261.10
Mepanipyrim
0.997
1010
3153
102
1692
13107
1116
330.83
Mesosulfuron-methyl0.997
810
2846
8215
104
593
612
350.94
Metazachlor
0.997
1110
2336
113
5100
593
612
160.90
S-Metolachlor
0.999
910
1826
938
927
977
1127
0.83
Metosulam
0.999
1110
3049
1109
948
888
1432
0.85
Metrib
uzin
0.999
1110
2133
105
1172
991
615
260.82
Mon
ocrotoph
os0.997
1210
2540
1154
100
388
314
320.90
Mon
olinuron
0.997
1010
2846
104
1792
1490
813
280.83
Mon
uron
0.997
1110
3153
1148
102
494
513
350.92
Ometho
ate
0.997
1110
2846
105
994
991
813
390.85
Oxadiargyl
0.997
1110
2336
105
15110
1190
1114
300.99
Oxadiazon
0.997
1010
3049
968
112
5112
56
321.0
1Oxadixyl
0.997
1110
2133
109
1290
1088
68
350.81
Oxamyl
0.997
1010
3049
103
1496
1289
811
330.86
Oxasulfu
ron
0.997
1110
3356
108
886
887
712
280.82
Oxycarboxin
0.997
1210
2846
115
7112
497
612
281.0
1Oxyflu
orfen
0.997
910
3049
928
101
7103
611
280.91
Pencon
azole
0.997
1110
2336
1127
102
496
49
280.92
Pend
imethalin
0.997
1110
2030
113
8108
5108
46
280.97
Pethoxam
id0.997
1110
2846
108
976
481
514
320.83
Phosalon
e0.998
1010
2336
9611
112
4112
58
361.0
1Ph
enmedipham
0.998
1010
3662
9514
9213
886
1130
0.83
Phenthoate
0.997
1210
2336
115
794
589
612
280.85
Phosmet
0.997
1010
2133
100
1194
1092
913
330.85
Phosph
amidon
0.997
1010
2133
998
108
795
710
300.97
Piclo
ram
0.997
1110
2133
105
1296
891
712
360.86
Picolin
afen
0.997
1010
2540
100
12114
9104
912
251.0
3Pirim
icarb
0.997
1210
2336
1198
942
973
1030
0.85
Pirim
ipho
s-methyl
0.997
1210
2336
115
7108
594
512
300.97
Prochloraz
0.999
1210
2133
115
5112
594
518
301.0
1Profenofos
0.999
1210
2133
115
7104
596
58
300.94
Prom
etryn
0.999
1110
2133
109
794
599
69
360.85
Prop
amocarb
0.998
1010
2540
100
13102
1089
911
300.92
Prop
anil
0.999
1210
3049
115
7102
599
612
280.92
Prop
argite
0.999
1010
2643
102
14112
10113
48
301.0
1Prop
ham
0.999
1010
2133
102
13100
696
510
280.90
Prop
icon
azole
0.999
1010
3049
986
122
4111
614
301.10
Prop
yzam
ide
0.999
810
2846
8410
969
955
933
0.86
14 Journal of Analytical Methods in Chemistry
Table2:Con
tinued.
Com
poun
ds𝑟2
LOQ
MRL
CC𝛼
CC𝛽
%recovery
%RS
D%recovery
%RS
D%recovery
%RS
D%RS
Dr
Relativ
eMatrix
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
10(𝜇g/kg)
10(𝜇g/kg)
25(𝜇g/kg)
25(𝜇g/kg)
50(𝜇g/kg)
50(𝜇g/kg)
uncertainty%
effect
Pymetrozine
0.997
1010
2336
101
1096
890
711
280.86
Pyraclo
strobin
0.997
1210
2133
115
7130
5119
415
261.17
Pyrid
aben
0.997
910
2030
8916
8012
814
1136
0.82
Pyrid
aphenthion
0.997
1010
2336
9911
120
999
1013
261.0
8Py
ridate
0.998
1010
3153
985
106
498
38
320.96
Pyrip
roxyfen
0.997
1010
2133
101
1194
686
513
220.85
Quinalpho
s0.997
1010
2336
101
576
690
514
230.82
Quino
xyfen
0.999
1010
3049
995
981
100
28
230.88
Quizalofop-P-ethyl
0.997
1210
3049
115
782
585
514
260.84
Rimsulfu
ron
0.998
910
2643
8813
104
3100
214
260.94
Simazine
0.997
1110
2336
106
1696
899
311
230.86
Spiro
xamine
0.999
810
2133
8314
849
822
1432
0.82
Sulfo
sulfu
ron
0.997
810
2133
8212
110
6111
619
300.99
Tebu
conazole
0.999
1010
2846
9910
946
995
925
0.85
TEPP
0.997
910
2336
907
107
7105
611
290.96
Terbutryn
0.997
1210
2643
115
896
5102
311
280.86
Terbuthylazine
0.997
1010
2030
104
12118
5116
46
261.0
6Tetrachlorvinp
hos
0.997
1110
2133
113
1178
890
414
280.90
Thiabend
azole
0.997
1210
2133
118
698
496
513
300.88
Thiaclo
prid
0.997
1110
1826
106
1384
1289
58
350.82
Thiametho
xam
0.997
1010
3356
104
19118
11113
811
321.0
6Th
ifensulfuron-methyl0.997
910
2030
9116
988
929
1530
0.88
Thiodicarb
0.997
1210
3153
115
7102
597
69
350.92
Thioph
anate-methyl
0.997
1110
2030
1149
112
695
513
321.0
1Triadimefon
0.997
1010
2846
104
7106
698
58
320.96
Triadimenol
0.997
1110
2540
107
14106
692
79
260.96
Triallate
0.998
1110
2336
106
9114
3111
412
301.0
3Triasulfu
ron
0.998
1110
2030
111
876
591
614
300.82
Triazoph
os0.998
1210
3049
115
796
587
59
300.86
Tribenuron
-methyl
0.998
1010
3559
999
103
8101
511
300.93
Tributylph
osph
ate
0.997
1010
1723
104
1488
1289
58
350.81
Journal of Analytical Methods in Chemistry 15
Table2:Con
tinued.
Com
poun
ds𝑟2
LOQ
MRL
CC𝛼
CC𝛽
%recovery
%RS
D%recovery
%RS
D%recovery
%RS
D%RS
Dr
Relativ
eMatrix
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
(𝜇g/kg)
10(𝜇g/kg)
10(𝜇g/kg)
25(𝜇g/kg)
25(𝜇g/kg)
50(𝜇g/kg)
50(𝜇g/kg)
uncertainty%
effect
Trichlorfon
0.998
1010
2540
9810
104
3100
214
270.94
Tridem
orph
0.997
1010
2133
9817
9013
100
511
300.81
Trifloxystro
bin
0.997
1210
2540
115
7124
5114
514
301.12
Triflum
izole
0.997
1110
2030
113
1492
599
58
280.83
Triticonazole
0.998
1010
1723
100
11106
1098
77
320.96
Vamidothion
0.997
910
2133
9313
118
6102
716
281.0
6Zo
xamide
0.997
1210
2336
116
772
485
315
250.82
Ciprofl
oxacin
0.997
7100
124
148
7425
6116
9713
938
0.81
Clindamycin
0.997
1110
1214
110
23106
15109
1012
340.96
Chlortetracycline
0.999
10100
108
116101
793
799
69
140.84
Danofl
oxacin
0.999
1030
4048
104
1487
1288
89
240.82
Difloxacin
0.999
910
1113
878
100
796
610
150.90
Doxycyclin
ehydrate
0.999
10100
110119
104
1493
1196
810
230.84
Flum
equine
0.998
950
5458
8812
105
1193
1011
220.95
Josamycin
0.998
910
1113
8812
104
1197
912
220.94
Lomefloxacin
0.999
1010
1213
9913
8911
998
1022
0.80
Orbifloxacin
0.999
910
1112
9314
107
894
711
200.96
Oxolin
icacid
0.999
1110
1215
110
12102
10102
615
200.92
Oxytetracyclin
e0.999
11100
111
122
11415
104
1295
610
230.94
Rifampicin
0.997
1010
1113
989
858
985
915
0.81
Saraflo
xacin
0.997
1010
1214
101
1097
8102
511
160.87
Sulfachloropyrid
azine
0.997
9100
116132
8813
106
1280
910
240.96
Sulfaqu
inoxaline
0.998
10100
111
122
9715
9910
789
924
0.89
Sulfadiazine
0.997
8100
108
116
8512
989
985
1018
0.88
Sulfamerazine
0.999
8100
111
122
8512
104
875
79
190.94
Sulfathiazole
0.999
9100
113
126
8511
109
1081
1017
210.98
Sulfamethazine
0.999
8100
114129
8413
104
9104
811
210.94
Sulfado
xine
0.999
9100
114129
8816
9512
956
1024
0.86
Sulfapyrid
ine
0.997
8100
119138
8311
108
1096
810
200.97
Sulfaclo
zine
0.998
10100
111122
9910
928
985
916
0.83
Sulfametho
xazole
0.998
10100
116
132
102
995
787
59
150.86
Tilm
icosin
0.999
1050
5662
9812
104
9105
410
180.94
Tetracyclin
e0.999
10100
119138
100
1884
896
59
230.82
16 Journal of Analytical Methods in Chemistry
calibration curves were established with and without matrix.Matrix-induced effectswere assessed by comparing the slopesof these calibration curves using the following formula:matrix effect (ME) = 1− (𝑎matrix/𝑎standard) × 100, where 𝑎matrixand 𝑎standard are the slopes of calibration straight lines forstandard andmatrix-matched calibration graphs.Thematrix-matched calibration curves were constructed using milksamples (5 g/mLmatrix equivalent) prepared inMeOH-watersolution with 0.1% acetic acid and spiked with veterinarydrug and pesticides at concentration levels of 0.01, 0.025,and 0.05mg/kg. Matrix effect was further evaluated for ionsuppression between the standards prepared in pure solventand standards prepared in matrix and the matrix effect wasfound to be in a range of 15–25%. These results showedthat standard calibration which was simpler and less time-consuming compared with matrix-matched calibration caneffectively be used for quantitation of veterinary drug andpesticides in milk (Table 2).
3.4. Real Samples. Themethod used analyzed more than 220milk samples submitted to the laboratory for veterinary drugand pesticide residues by the local markets. Two transitionion pairs were monitored for each of the analytes and the ionratios of detected samples were compared well with those ofstandards. Retention times of analytes were also confirmedby addition of known standards in detected samples. Eightsamples out of 220 milk samples were found to containresidues of veterinary drug and pesticide residues (4% inci-dence was positive). Sulfadiazine (veterinary drug) residueamountwas found between 0.075 and 0.125mg/L in 2 samplesand tetracycline (veterinary drug) amount was found to be0.015–0.100mg/L in 4 samples. Carbaryl (pesticide) residueconcentration level was 0.005–0.025mg/L in 2 samples.
4. Conclusions
Amulticlass/multiresidue procedure with LC-MS/MS detec-tion has been developed and validated to determine andquantify veterinary and pesticide residues in milk. A simplesample preparationmethod involved liquid extraction saltingout procedures in ethyl acetate system, without cleanup steps,and shortening the sample preparation time. Validation of themethod was performed according to Commission Decision2002/657/EC. The method was characterized by good resultsin terms of recovery, reproducibility, and repeatability allow-ing the detection of veterinary drug and pesticide residuesbelow the recommended analytical level. Based on theseresults, LC-MS/MS method with ethyl acetate extractionshowed the suitability for sensitive quantification of veteri-nary and pesticide residues in milk samples for food safetyapplications. The validated method was applied on 220 realcommercial samples. This short protocol can be applicableto a large number of samples for routine analysis and rapiddetection.
Competing Interests
The authors declare that there are no competing interestsregarding the publication of this paper.
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