Authors |
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Fred Foster & Virgil Settle, Paul Roberts, Peter Stone, Joan Stevens, Jon Wong, Kai Zhang, |
Figure 1. Representative Mass Chromatograms for low QC sample.
Figures 2 through 4 show representative overlay mass chromatograms of neat, hop matrix matched, and ginseng matrix matched calibration standards respectively at 10 ppb. The standards were prepared automatically by the MPS XL.
Figure 3. Representative overlay mass chromatogram for a 10 ppb hop matrix matched standard.
Figure 4. Representative overlay mass chromatogram for a 10 ppb ginseng matrix matched standard.
Figure 5. shows a representative calibration curve resulting from automated preparation of neat standards. The calibration curves were shown to be linear from at least 1.00 to 200 ppb for the pesticides monitored, using a linear, 1/x regression method.
Automated QuEChERS extract
clean-up for LC-MS/MS
So long, troublemakers II
LC/MS and GC/MS systems are increasingly confronted with QuEChERS extracts that have to be cleaned prior to determination of pesticide residues in order to avoid build-up of matrix residue in the analysis system. Automated QuEChERS extract clean-up, including vortexing, centrifugation, and filtration directly followed by LC-MS/MS analysis of the cleaned extract is demonstrated in this article.
The QuEChERS (quick, easy, cheap, effective, rugged, and safe) sample extraction method offers food safety laboratories a novel method that is a genuine step forward. QuEChERS is now the basis for efficient monitoring of pesticides in an evergrowing range of foods. Still, the method is quite labor intensive with several manual steps such as shaking, centrifugation, and dispersive SPE. If the dispersive SPE clean-up step could be automated, laboratory productivity could be improved significantly. When using the automated QuEChERS clean-up procedure for challenging botanical samples, it can be difficult to reach the low limits of detection required in order to meet acceptance criteria for reporting the maximum residue levels (MRLs) as established by regulatory agencies. Automated QuEChERS clean-up of fruit and vegetable extracts combined with LC-MS/MS determination of pesticides has been reported previously.
This study focuses on using a similar system to automate the second step of the QuEChERS procedure and introduce the cleaned extract directly to an LC-MS/MS system. The aim is to provide high throughput analysis for the confirmation of pesticide residues in botanical matrices. Automated QuEChERS extractions are performed using a QuEChERS dispersive SPE sorbent blend for fatty matrices.
Experimental
Stock solutions containing the pesticide compounds listed in Table 1 in acetonitrile were prepared and provided by the FDA. Calibration standards and matrix matched standards were prepared by making appropriate dilutions of the pesticide stock solutions using mobile phase, blank hop extract, or blank ginseng extract resulting in the following concentrations: 0.5, 1, 2, 5, 10, 20, 50, 100, 200, 500, and 1000 ng/mL. Crude acetonitrile extracts of pesticide-fortified samples, incurred samples, and blank matrix samples based on both hops and ginseng root were prepared and provided by the FDA. These samples were generated using QuEChERS extraction salts for the DIN EN 15662 Method and the recommended sample preparation method supplied with the salts. All automated PrepSequences were performed using a MultiPurpose Sampler (MPS XL Dual Head) configured for QuEChERS-LC- MS/MS analysis.
QuEChERS extract pretreatment:
- Pipette 1 mL of the acetonitrile extract obtained following the 1st centrifugation step of the QuEChERS sample preparation method into a 2 mL glass autosampler vial containing a sorbent from a dispersive SPE kit for fatty samples, AOAC.
- Place the sample onto a tray on the GERSTEL MPS XL Dual Head.
Automated QuEChERS extract clean-up:
- Agitate the sample vial for 1 minute using the Anatune CF-100 centrifuge.
- Centrifuge the sample vial at 575 g for 3 minutes using the Anatune CF-100 centrifuge.
- Filter 500 μL of the resulting supernatant through a 0.45 μm GERSTEL format syringe filter.
- Combine 100 μL of the resulting filtrate with 400 μL of mobile phase A in a clean 2 mL vial.
- Agitate the sample vial using the Anatune CF-100 centrifuge for 30 seconds. Inject 2 μL into the LC-MS/MS system.
Preparation of all standards was automated using the MPS XL Dual Head as follows:
- Transfer 100 μL of previously extracted matrix blank or 100 % acetonitrile to an empty 2 mL autosampler vial.
- Transfer 250 μL of mobile phase A to the vial.
- Transfer 150 μL of the respective standard stock solution to the vial.
- Agitate the vial using the Anatune CF-100 and centrifuge for 30 seconds.
All analyses were performed using an Agilent 1290 HPLC, an Agilent 6460 Triple Quadrupole Mass Spectrometer with electrospray source and Jet Stream Option and a GERSTEL MPS XL autosampler configured with Active Wash Station. Sample injections were made using a 6 port (0.25 mm) Cheminert C2V injection valve fitted with a 2 μL stainless steel sample loop. The mass spectrometer acquisition parameters and respective quantifier/ qualifier ion transitions were chosen using the pesticide database option available for the MassHunter B.03.01 software. Table 1 provides a list of the more than 200 pesticides that were monitored using this single LC-MS/MS method. A retention time window value of 0.5 minute was used for each positive ion transition being monitored during the course of the dynamic MRM experiment.
Analysis conditions LC |
| Mobile Phase: A - 5 mM ammonium formate in water with 0.01 % formic acid B – 0.01 % formic acid in acetonitrile Gradient: Initial 94 % A / 6 % B 0.3 min 94 % A / 6 % B 14 min 5 % A / 95 % B 17 min 5 % A / 95 % B Pressure: 600 bar Flowrate: 500 μL/min Runtime: 17 min Post time: 2.5 min Column: 2.1 mm x 100 mm, 1.8 μm, Zorbax Eclipse+ C18 RRHT (Agilent) Oven: 55°C Injection volume: 2 μL |
Analysis conditions MS |
| Operation: ESI+ mode (Jet Stream) Time Filter Width: 0.04 min Scan Type: Dynamic MRM Delta EMV: 0 V Cycle Time: 660 ms Gas Temperature: 225 °C Gas Flow (N2): 10 L/min Nebulizer pressure: 25 psi Sheath Gas (N2): 350 °C 11 L/min Capillary voltage: 4500 V Nozzle Voltage: 500 V |
Results and discussion
Figures 1 - 4 show representative overlay mass chromatograms resulting from QuEChERS extracts of pesticide-fortified samples. More than 200 different pesticides were successfully determined in botanical matrices using the automated QuEChERS-LC-MS/MS method.
The total time required per sample to perform the QuEChERS extract clean-up was 15 minutes. This was shorter than the LC-MS/MS analysis run, enabling the MPS system to complete preparation of the next sample during the LC-MS/MS run for maximum sample throughput.
Conclusion
The study has demonstrated:
- Successful monitoring of more than 200 pesticides in botanical matrix samples using automated QuEChERS extract clean-up coupled with LC-MS/MS analysis using the Agilent 6460 Triple Quadrapole Mass Spectrometer.
- Automation of both the QuEChERS extract clean-up and the preparation of standards using the GERSTEL MPS XL Dual Head robotic sampler.
- The “just-in-time” sample preparation capability included in the MAESTRO software enables highly efficient QuEChERS extract clean-up and analysis.
| 3-Hydroxycarbofuran | Acephate | Acetamiprid | Acibenzolar-S-methyl | Alanycarb |
| Aldicarb | Aldicarbsulfone | Aldicarb sulfoxid | Aspon | Avermectin B1a |
| Avermectin B1b | Azadirachtin | Azoxystrobin | Benalaxyl | Bendiocarb |
| Benfuracarb | Benoxacor | Benthiavalicarb | Benzoximate | Bifenazate |
| Bifenthrin | Bitertanol | Boscalid | Bromuconazole-1 | Bromuconazole-2 |
| Bupirimate | Buprofezin | Butafenacil | Butocarboxym | Butoxycarboxim |
| Cadusafos | Carbaryl | Carbendazim | Carbetamid | Carbofuran |
| Carboxine | Carfentrazone-ethyl | Chlordimeform | Chlorfenvinphos-beta | Chlorfluazuron |
| Chlorotoluron | Chloroxuron | Clethodim | Clofentezine | Clothianidin |
| Coumaphos | Cumyluron | Cyanazine | Cyanophos | Cyazofamid |
| Cycluron | Cymoxanil | Cyproconazole | Cyprodinil | Cyromazine |
| d10-Diazinon | d6-Dichlorvos | d6-Dimethoate | d6-Diuron | d6-Linuron |
| d6-Malathion | Daimuron | Dazomet | Deltamethrin | Diazinon |
| Dichlorvos | Dicrotophos | Diethofencarb | Difenoconazol | Diflubenzuron |
| Dimethenamid | Dimethoat | Dimethomorph A | Dimethomorph B | Dimoxystrobin |
| Diniconazole | Dinotefuran | Dioxacarb | Disulfoton | Dithiopyr |
| Diuron | Dodemorph 1 | Dodemorph 2 | E-Fenpyroximate | Emamectin B1a |
| Emamectin B1b | Epoxiconazole | Eprinomectin B1a | EPTC | Esprocarb |
| Ethidimuron | Ethiofencarb | Ethion | Ethiprole | Ethirimol |
| Ethofumesate | Ethoprop | Etobenzanid | Etofenprox | Etoxazole |
| Famoxadone | Fenamidone | Fenarimol | Fenazaquin | Fenbuconazol |
| Fenhexamid | Fenoxanil | Fenoxycarb | Fenpropathrin | Fenpropimorph |
| Fenuron | Flonicamid | Flucarbazone | Fludioxinil | Flufenacet |
| Flufenoxuron | Flumetsulam | Flumioxazin | Fluometuron | Fluquinconazole |
| Flusilazol | Fluthiacet-methyl | Flutolanil | Flutriafol | Forchlorfenuron |
| Formetanate | Fuberidazole | Furalaxyl | Furathiocarb | Heptenophos |
| Hexaconazol | Hexaflumuron | Hexythiazox | Hydramethylnon | Imazalil |
| Imazapyr | Imibenconazole | Imidacloprid | Indanofan | Indoxacarb |
| Ipconazole | Iprovalicarb | Isocarbamid | Isofenfos | Isopropalin |
| Isoproturon | Isoxaben | Isoxaflutole | Kresoxim-methyl | Lactofen |
| Leptophos | Linuron | Lufenuron | Mandipropamid | Mefenazet |
| Mepanipyrim | Mepronil | Metalaxyl | Metconazole | Methabenzthiazuron |
| Methamidophos | Methiocarb | Methomyl | Methoprotryne | Methoxifenozid |
| Metobromuron | Metribuzin | Mevinphos | Mexacarbate | Molinate |
| Monocrotophos | Monolinuron | Moxidectin | Myclobutanil | Neburon |
| Nitenpyram | Norflurazon | Novaluron | Nuarimol | Omethoate |
| Oxadixyl | Oxamyl | Paclobutrazol | Penconazole | Pencycuron |
| Phenmedipham | Picoxystrobin | Piperonyl butoxide | Pirimicarb | Prochloraz |
| Promecarb | Prometon | Prometryn | Propachlor | Propamocarb |
| Propargite | Propazine | Propham | Propiconazole | Propoxur |
| Pymetrozine | Pyracarbolid | Pyraclostrobin | Pyridaben | Pyrimethanil |
| Pyriproxyfen | Quinoxyfen | Rotenone | Sebuthylazine | Secbumeton |
| Siduron | Simazine | Simetryn | Spinosyn A | Spinosyn D |
| Spirodiclofen | Spiromesifen | Spiroxamin | Sulfentrazone | Tebuconazole |
| Tebufenozide | Tebufenpyrad | Tebuthiuron | Teflubenzuron | Temephos |
| Terbumeton | Terbutryn | Terbutylazine | Tetraconazole | Tetramethrin cis |
| Thiabendazole | Thiacloprid | Thiametoxam | Thiazopyr | Thidiazuron |
| Thiobencarb | Thiofanox | Thiophanate-methyl | Triadimefon | Triadimenol |
| Trichlamide | Trichlorfon | Tricyclazole | Trifloxystrobin | Triflumizole |
Table 1. 200+ pesticides monitored using automated QuEChERS extract clean-up.
Literature:
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AppNote-2010-04 Automated QuEChERS Extraction for the Confirmation of Pesticide Residues in Foods using LC/MS/MS |





