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Acknowledgements:
A special thanks to Dr. Michelle Ward, Dr. Rena Robinson, Christina King,
Liqing Gu, Yaphet Geadion, Lindsay Osentoski, and the company sponsors who
made this session possible.
References:
(1) Garcia-Reyes, Juan, Ayanna Jackson, Antonio Molina-Diaz, and R. Cooks. "Desorption Electrospray
Ionization Mass Spectrometry for Trace Analysis of Agrochemicals on Food." American Chemical Society 81.2
(2008): 820-29. Analytical Chemistry. ACS. Web. 27 Sept. 2015.
<http://pubs.acs.org/doi/pdf/10.1021/ac802166v>.
(2) http://webbook.nist.gov/chemistry/
(3) http://www.chm.bris.ac.uk/ms/theory/esi-ionisation.html
Background
• An ESI-MS determines the mass-to-charge ratio by pumping the
sample solution through the capillary needle which results in the
charged spray of fine droplets. The resulting gaseous ions are
analyzed by the detector.
Experimental Design
Discussion
Conclusion
• The data could have been better quantified if an
internal standard was used and the ESI-MS
was coupled with the LC-MS.
• Further studies can be completed by analyzing
different pesticides, produce, and instrument
schemes.
• Some sources of error could have resulted in
the analyte concentrations being lower than
their LOD.
Introduction
• The purpose of this experiment was to detect
trace amounts of various insecticides and
fungicides on different types of produce since
the presence of these chemicals and their
degradation products could cause potential
health hazards1.
• An Electrospray Ionization mass spectrometer
was used for the identification of the various
agrochemicals in both the standard and
produce samples.
Figure 2: Ions were produced by applying a
voltage to the sample and an aerosol was created.
Figure 1: ESI MS used direct infusion with LTQ
ion trap with Finnigan Ion Max API source.
The Thermo Finnigan LTQ MS was used with the
following parameters: ESI+ Mode, Nitrogen Gas,
Full Scan Mode, 500 Scans, 150-2000 m/z range.
15 g of
homogenized
subsample
15 mL ACN
Shake 1 min
6 g MgSO4
1.5 g NaCl
Shake 20 sec
Centrifuge
3.7K rpm for
1 min
750 mg
MgSO4
150 mg PSA
Shake 20 sec
Centrifuge
3.7K rpm for
1 min
1 g of sample
in 100% ACN
Results
Analyte
202.0
(m/z)
293.1
(m/z)
297.1
(m/z)
306.2
(m/z)
404.1
(m/z)
Kale
(ppb)
0.9507 0.3415 2.2782 0.4711 0.0000
Apple
(ppb)
0.6342 0.0000 3.6492 0.6703 11.6670
Organic
Apple
(ppb)
0.4037 0.0000 7.8169 0.0000 2.8863
Spinach
(ppb)
4.0446 0.2367 2.3677 3.5713 2.4787
Organic
Spinach
(ppb)
0.0000 0.0000 0.0000 0.0000 0.0000
Orange
(ppb)
0.6282 0.0000 0.7045 0.0000 0.9824
Orange
Peel
2.4974 0.2825 2.6197 0.0000 11.8972
LOD
(ppb)
15.0000 2.0000 4.0000 5.0000 8.0000
Figure 3: Schematic of the Linear Ion Trap
Detector that was used to analyze the ions.
Figure 4: Mass Spec of Thiabendazole Standard, 199 – 208 m/z.
Figure 4: ESI-MS Spectra for orange and orange
peel samples, 195-415 m/z.
Figure 5: Identification of Thiabendazole in
orange and orange peel samples, 201.8-202.8 m/z.

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poster esi

  • 1. Acknowledgements: A special thanks to Dr. Michelle Ward, Dr. Rena Robinson, Christina King, Liqing Gu, Yaphet Geadion, Lindsay Osentoski, and the company sponsors who made this session possible. References: (1) Garcia-Reyes, Juan, Ayanna Jackson, Antonio Molina-Diaz, and R. Cooks. "Desorption Electrospray Ionization Mass Spectrometry for Trace Analysis of Agrochemicals on Food." American Chemical Society 81.2 (2008): 820-29. Analytical Chemistry. ACS. Web. 27 Sept. 2015. <http://pubs.acs.org/doi/pdf/10.1021/ac802166v>. (2) http://webbook.nist.gov/chemistry/ (3) http://www.chm.bris.ac.uk/ms/theory/esi-ionisation.html Background • An ESI-MS determines the mass-to-charge ratio by pumping the sample solution through the capillary needle which results in the charged spray of fine droplets. The resulting gaseous ions are analyzed by the detector. Experimental Design Discussion Conclusion • The data could have been better quantified if an internal standard was used and the ESI-MS was coupled with the LC-MS. • Further studies can be completed by analyzing different pesticides, produce, and instrument schemes. • Some sources of error could have resulted in the analyte concentrations being lower than their LOD. Introduction • The purpose of this experiment was to detect trace amounts of various insecticides and fungicides on different types of produce since the presence of these chemicals and their degradation products could cause potential health hazards1. • An Electrospray Ionization mass spectrometer was used for the identification of the various agrochemicals in both the standard and produce samples. Figure 2: Ions were produced by applying a voltage to the sample and an aerosol was created. Figure 1: ESI MS used direct infusion with LTQ ion trap with Finnigan Ion Max API source. The Thermo Finnigan LTQ MS was used with the following parameters: ESI+ Mode, Nitrogen Gas, Full Scan Mode, 500 Scans, 150-2000 m/z range. 15 g of homogenized subsample 15 mL ACN Shake 1 min 6 g MgSO4 1.5 g NaCl Shake 20 sec Centrifuge 3.7K rpm for 1 min 750 mg MgSO4 150 mg PSA Shake 20 sec Centrifuge 3.7K rpm for 1 min 1 g of sample in 100% ACN Results Analyte 202.0 (m/z) 293.1 (m/z) 297.1 (m/z) 306.2 (m/z) 404.1 (m/z) Kale (ppb) 0.9507 0.3415 2.2782 0.4711 0.0000 Apple (ppb) 0.6342 0.0000 3.6492 0.6703 11.6670 Organic Apple (ppb) 0.4037 0.0000 7.8169 0.0000 2.8863 Spinach (ppb) 4.0446 0.2367 2.3677 3.5713 2.4787 Organic Spinach (ppb) 0.0000 0.0000 0.0000 0.0000 0.0000 Orange (ppb) 0.6282 0.0000 0.7045 0.0000 0.9824 Orange Peel 2.4974 0.2825 2.6197 0.0000 11.8972 LOD (ppb) 15.0000 2.0000 4.0000 5.0000 8.0000 Figure 3: Schematic of the Linear Ion Trap Detector that was used to analyze the ions. Figure 4: Mass Spec of Thiabendazole Standard, 199 – 208 m/z. Figure 4: ESI-MS Spectra for orange and orange peel samples, 195-415 m/z. Figure 5: Identification of Thiabendazole in orange and orange peel samples, 201.8-202.8 m/z.