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©2015 Waters Corporation 1
Ultra-Trace Level Quantitative Analysis of Food
Contaminants using LC and GC coupled to MS
©2015 Waters Corporation 2
Overview
 Ultra-trace residue analysis in food
– What are the challenges?
 Persistent organic pollutants in foods
 LC & GC source interfaces & options
– Universal source interface
– Introduction to the Xevo-TQ-S
 Principles of APGC
– How does it work?
– Multi-residue pesticide analysis (LC & GC amenable)
– Commission Regulation 589/2014
– APGC for dioxins
 Summary and conclusions
©2015 Waters Corporation 3
Residue & contaminant analysis challenges?
Matrix &
analyte
complexity
Sample type &
extract
preparation
Ease of use &
implementation
Compliance with
regulatory
performance
criteria
Validation &
AQC
requirements
©2015 Waters Corporation 4
Analysis of POPs
Requirement for both LC & GC
 Stockholm convention
– Global agreement to reduce environmental POPs levels
– 12 classes of compounds listed
– Persistent environmental pollutants
 Dioxins: HR-GC-MS (magnetic sector)
 BFRs: PBDEs: HR-GC-MS or GC-MS/MS
 PFCs: LC-MS/MS
 Endocrine disruptors: LC-MS/MS & GC-MS/MS
 Nitrosamines: GC-MS/MS
 Legacy pesticides: LC-MS/MS & GC-MS/MS
O
BrBr
Br
Br
Br
Br
Br
Br
Br
Br
Cl
Cl
O
O
Cl
Cl
F
F
F
F
F
F
F
F
F
S
O
OF F
F
F
F
F
FF OH
Br
Br
Br
Br
Br
Br
Cl
Cl
O
Cl
Cl
Cl Cl
©2015 Waters Corporation 5
LC and GC Source Interfaces and
Options
©2015 Waters Corporation 6
The Universal Source – configurations
and options
LC
©2015 Waters Corporation 7
APGC Overview
 Waters APGC is an optional ion source for Xevo systems that provides
a highly sensitive GC-MS, MS/MS capability
 Very easy to swap between APGC, UPLC, other ion sources without
instrument venting in minutes
 APGC ionisation is soft (cf. APCI) and molecular ions are readily
detected
 Fragmentation can be induced (CID) to provide information for
structural elucidation
 Xevo tandem quad (Xevo TQ-S) is a powerful tool for routine
quantitation coupled to both LC & GC
– Capability of using the RADAR for exploratory experiments
©2015 Waters Corporation 8
APGC coupled to Xevo TQ-S
- enhanced sensitivity tandem quadrupole-
MS
©2015 Waters Corporation 9
Xevo TQ
Xevo TQ-S
StepWave
ScanWave
(Collision cell)
How did we increase sensitivity?
Hexapole
(Transfer Optics)
1st Quadrupole
(Precursor ion selection)
2nd Quadrupole
(Product ion selection)
Larger sampling cone aperture = 200x increase in ion flux
©2015 Waters Corporation 10
ElectricField
Diffuse
Ion
Cloud
Maximising signal
Maximising robustness
Designed to deal with problems
associated with a larger sampling orifice
Compact
ion cloud
©2015 Waters Corporation 11
LC and GC on one instrument
Sensitive and robust
GC
LC
©2015 Waters Corporation 12
LC and GC on one instrument
Is it possible?
ESI
©2015 Waters Corporation 13
LC and GC on one instrument
Is it possible?
APGC
©2015 Waters Corporation 14
Atmospheric Pressure Gas Chromatography
(APGC)
How does it work?
©2015 Waters Corporation 15
Universal Source
ESI and APGC modifications fitted
Sampling
cone
Electrospray Configuration
Vial containing
modifier
Ion chamber &
corona pin
APGC Configuration
APGC source door
Entrance for transfer line
©2015 Waters Corporation 16
Source and Ion Chamber
©2015 Waters Corporation 17
Remove the source housing
Plinth mounting – helps
ensure correct alignment of
the transfer line to the source
GC 7890
Exchange between LC and GC
No venting required
©2015 Waters Corporation 18
Slide the GC
©2015 Waters Corporation 19
Ready for GC/MS
©2015 Waters Corporation 20
Mass Spec
Corona Pin
Atmospheric
Region
Heated Transfer Line
Capillary
GC Column
Ionization
Chamber
APGC Source Schematic
©2015 Waters Corporation 21
Corona Pin
Creates
corona
discharge at
the needle
Atmospheric Pressure Source
Capillary
GC Column
Ionization Chamber
Ionisation occurs either by charge transfer
or proton transfer depending on the
conditions in the source
Heated Transfer Line
Transfer Line GC
Make up (sheath) gas
N2 250 ml/min
together with cone gas
supplies nitrogen for
the plasma
Mass
Spectrometer
APGC – How it works
©2015 Waters Corporation 22
Mass Analyser GC Oven
Corona discharge
at needle creates plasma
N2 make-up
(250ml/min) gas
delivered
through transfer line
interior
N2 meets GC eluent flow
at transfer line tip
Analyte Molecules are ionised after
GC elution and directed to the mass analyser
APGC – How it works
©2015 Waters Corporation 23
APGC Ionisation Modes & Advantages
©2015 Waters Corporation 24
Mechanism of Ionisation (I)
N2
+●
N2e-
2e-
2N2
N4
+● M●+
M
Corona Pin
M●+
M
Charge Transfer
 “Dry” source conditions
 Favored by relatively non-polar compounds
©2015 Waters Corporation 25
Mechanism of Ionisation (II)
N2
+●
N4
+●
H2O
H2O+●
H2O
H3O+●
+OH●
[M+H]+
M
Protonation
 Modified source conditions eg. with water or methanol present
 Favored by relatively polar compounds
Corona Pin
©2015 Waters Corporation 26
Time
2.00 4.00 6.00 8.00 10.00 12.00 14.00
%
0
100
ANAPGC240409TEST009 TOF MS AP+
278.025 0.02Da
671
8.75
0.01µg/ml BF Std
Time
8.00 10.00 12.00 14.00 16.00 18.00 20.00 22.00
%
0
100
CSL_200306_204 TOF MS EI+
277.018 0.02Da
298
15.98
EI GC
5uL Injection
APGC
1uL Injection
298cps
EI+
671cps
AP+
Faster run possible due
to atm pressure source
and higher res MS
15.98
8.75
~ 10X higher
response for APGC
Chromatographic Performance
Flow rate
©2015 Waters Corporation 27
EI GC/MS compared to APGC-MS
Parameter GC/MS APGC
Linearity ✔ ✔
Sensitivity ✔ ✔
NIST Library Spectra ✔ ✘
Ease of Use ✘ ✔
Matrix Tolerance ✘ ✔
Low fragmentation spectra ✘ ✔
Access to latest MS innovations ✘ ✔
©2015 Waters Corporation 28
APGC-TQ-S
Complete solution for targeted multi-class
pesticide residue analysis
Circa 60% of pesticides tested in EU require LC-MS &
40% require GC-MS
©2015 Waters Corporation 29
NIST EI
Spectrum
APGC
Spectrum
Endosulphan
M+.
The challenge...
©2015 Waters Corporation 30
Strategy for analysis of LC & GC
amenable pesticides
©2015 Waters Corporation 31
SPE for GC-MS Tea Analysis
©2015 Waters Corporation 32
“Difficult” pesticide comparison
EI-GC & APGC
tR Compounds Molecular formula M EI APGC APGC+H2O
M•+ M•+ MH+ MH+
4.70 Dichlorvos C4H7Cl2O4P 220 +++ +++
5.97 Mevinphos C7H13O6P 224 ++ + ++
6.96 Molinate C9H17NOS 187 + +++ +++
8.00 Dicrotophos C8H16NO5P 237 + ++ ++ +++
8.24 Monocrotophos C7H14NO5P 223 + ++ ++ +++
8.95 Terbufos C9H21O2PS3 288 +
9.80 Phosphamidon C10H19ClNO5P 299 + ++ +++
9.76 Endosulfanether C9H6Cl6O 340 + + ++ ++
9.94 Chlorpyriphosmethyl C7H7Cl3NO3PS 321 ++ +++
10.77 Chlorpyriphos C9H11Cl3NO3PS 349 + +++ +++
10.85 Aldrin C12H8Cl6 362 + + ++
11.39 Isodrin C12H8Cl6 362 ++ ++ ++
11.56 Chlorfenvinphos C12H14Cl3O4P 358 ++ +++
11.56 Oxychlordane C10H4Cl8O 420 + + ++
11.56 HeptachlorepoxideB C10H5Cl7O 386 + + ++
12.23 EndosulfanI C9H6Cl6O3S 404 ++ ++
12.72 Buprofezin C16H23N3OS 305 + ++ +++ +++
12.73 Dieldrin C12H8Cl6O 378 + ++ ++ ++
13.10 Endrin C12H8Cl6O 378 ++ ++ ++
13.36 Ethion C9H22O4P2S4 384 + +++ +++
14.01 Endosulfansulfate C9H6Cl6O4S 420 ++ ++
15.63 Azinphosmethyl C10H12N3O3PS2 317 +
15.66 Pyriproxyfen C20H19NO3 321 ++ +++
16.04 Fenarimol C17H12Cl2N2O 330 + ++ +++ +++
16.17 Azinphosethyl C12H16N3O3PS2 345 +
+, very small peak; ++, clearly identifiable peak (>20%); +++, base peak (or >80%)
©2015 Waters Corporation 33
142 multi-class method for pesticides in
fruits & vegetables
 QuEChERS including a 10-fold dilution of the final
acetonitrile extract  direct injection splitless
 [M+H]+ precursor ions for most (90%) compounds
 3 SRM transitions /compound
Validation
 Spiked samples 0.01 and 0.1 mg/kg
 Quantification  matrix-matched calibration
 Ion ratio tolerances achieved
Application Of Gas Chromatography-(Triple Quadrupole) Mass Spectrometry With Atmospheric Pressure
Chemical Ionization For The Determination Of Multiclass Pesticides In Fruits And Vegetables, Laura Cherta et
al (2013) Journal of Chromatography A (1292) 132-141
©2015 Waters Corporation 34
% Recovery
%
Frequency
% % %
0
20
40
60
80
100
<70 70-110 110-120 >120
-10
10
30
50
70
90
110
130
<70 70-110 110-120 >120
0.01 mg/kg
0.1 mg/kg
% Recovery
(n=6)
1 pg injected
10 pg injected
Performance Data
Validation 142 pesticides in three different matrices
©2015 Waters Corporation 35
Authors’ Conclusions…
 APCI allows a “universal” soft-ionization for GC-amenable
compounds, which provides more selectivity and sensitivity
due to the selection of the molecular ion/protonated molecule
as precursor ion.
 GC-APCI-(QqQ) MS/MS presents good analytical
characteristics regarding linearity, precision and limits of
detection for determination of target residues in food and
environmental samples.
 The novel APCI source reveals itself as a good
choice to consider in GC-MS/MS for pesticide
residue analysis, as well as a suitable
alternative to HRMS in the dioxins field
©2015 Waters Corporation 36
Waters pesticide GC method
Summary of conditions & performance
Compound
MRM
Quantification
Retention time
(min)
Limit of
detection
(ng/mL)
Correlation
Coefficient (R2)
Aldrin 363>159 13.4 0.5 0.992
Azinphos-Ethyl 289>261 14.2 0.05 0.993
Azinphos-Methyl 261>125 20.0 0.5 0.990
Buprofezin 306>106 15.9 0.05 0.991
Chlorfenvinphos 359>170 14.3 0.05 0.994
Chlorpyriphos 350>198 13.2 0.1 0.995
Chlorpyriphos-Methyl 322>125 12.1 0.05 0.991
Dichlorvos 221>145 6.3 0.01 0.995
Dicrotophos 238>112 9.6 0.05 0.990
Dieldrin 379>325 16.0 0.1 0.995
Endosulfan I 405>323 15.3 0.1 0.992
Endosulfan-Ether 341>205 18.7 0.01 0.995
Endosulfan-Sulphate 323>217 17.7 0.05 0.992
Endrin 379>243 16.5 0.05 0.997
Ethion 385>143 16.8 0.05 0.996
Fenarimol 331>139 20.7 0.1 0.997
Heptachlor Epox B 387>217 17.7 0.1 0.992
Mevinphos 225>127 7.5 0.05 0.995
Phenthoate 321>135 14.4 0.05 0.993
Phosphamidon 300>127 12.0 0.1 0.993
Wet source conditions used [APGC +H2O], internal standard used
Application note reference: 720004776en
©2015 Waters Corporation 37
APGC linearity
Azinphos-methyl in strawberry extract,
triplicate injection internally standardised
R2 = 0.9975
©2015 Waters Corporation 38
APGC – Repeatability in matrix
Matrix matched standards at 1 μg/kg n=10
©2015 Waters Corporation 39
Dioxins & furans
EU legislation revision for screening &
confirmation June 2014
©2015 Waters Corporation 40
 Dioxins & dioxin-like compounds (DLC)
are by-products of various industrial
processes, and are commonly regarded
as highly toxic compounds that
are environmental and persistent
pollutants (POPs)
 Analysis must comply with legislative
requirements. EPA1613 in USA and (EC)
No 152/2009 & 589/2014 in Europe
 ‘Gold Standard’ is magnetic sector MS
(AutoSpec Premier)
 Regulation 589/2014 permits the use of
GC-MS/MS for both screening &
confirmatory purposes
Commission Regulation 589/2014
Screening & confirmatory methods
©2015 Waters Corporation 41
Analytical criteria for use of MS/MS for
determination of dioxin-like PCBs in feed & food
NEW EU LEGISLATION 02 June 2014
©2015 Waters Corporation 42
APGC application for dioxins & furans
 Charge transfer [M+·] precursor ions for all compounds
 2 SRM transitions / compound + labelled standards
Validation
 Analysis of certified reference material
 Quantification using commercial standard solutions
©2015 Waters Corporation 43
1368-TCDD
min. 2 fg
on column
1379-TCDD
1378-TCDD
1478-TCDD
1234-TCDD
2378-TCDD
TF-TCDD-MXB;
Components and Concentrations
(fg/µl, ± 5% in nonane)
Component Conc (fg/µl)
1368-TCDD 2
1379-TCDD 5
1378-TCDD 10
1478-TCDD 25
1234-TCDD 50
2378-TCDD 100
13
C-2378-TCDD 5
Sensitivity - TCDD mix
©2015 Waters Corporation 44
1368-TCDD
min. 2 fg
on column
1379-TCDD
1379-TCDD
1368-TCDD
1378-TCDD
1378-TCDD
1478-TCDD
1478-TCDD
1234-TCDD
1234-TCDD
2378-TCDD
2378-TCDD
GC-HRMS
GC-MS/MS (QqQ)
Sensitivity – comparison to GC-HRMS
©2015 Waters Corporation 45
1613 CSL 10-fold dilution 0.01 ng/mL
S/N ≈ 20
Precision - TCDD mix
©2015 Waters Corporation 46
Quantitative performance
Linearity over range 10 fg > 40 pg on-column
Compound %RSD Calibration
RRF
Coeff. Of
Determination
TCDD 3.3 >0.999
TCDF 7.9 >0.999
PCDD 2.8 >0.999
1,2,3,7,8-PCDF 2.8 >0.999
2,3,4,7,8-PCDF 2.1 >0.999
1,2,3,4,7,8-HxCDD 4 >0.999
1,2,3,6,7,8-HxCDD 4.1 >0.999
1,2,3,7,8,9-HxCDD 3.5 >0.999
1,2,3,4,7,8-HxCDF 6.3 >0.999
1,2,3,6,7,8-HxCDF 5 0.999
2,3,4,6,7,8-HxCDF 3 >0.999
1,2,3,7,8,9-HxCDF 8 0.998
1,2,3,4,6,7,8-HpCDD 5.8 >0.999
1,2,3,4,6,7,8-HpCDF 4 >0.999
1,2,3,4,7,8,9-HpCDF 3.3 >0.999
OCDD 1.8 >0.999
OCDF 8.3 0.998
Compound name: TCDD
Correlation coefficient: r = 0.999887, r^2 = 0.999774
Calibration curve: 1.02895 * x + -0.00220016
Response type: Internal Std ( Ref 1 ), Area * ( IS Conc. / IS Area )
Curve type: Linear, Origin: Exclude, Weighting: 1/x, Axis trans: None
pg/µL
-0.0 2.5 5.0 7.5 10.0 12.5 15.0 17.5 20.0 22.5 25.0 27.5 30.0 32.5 35.0 37.5 40.0
Response
-0.0
5.0
10.0
15.0
20.0
25.0
30.0
35.0
40.0
©2015 Waters Corporation 47
APGC-TQ-S comparison with
HR-GC/MS
Fish
0.00
0.20
0.40
0.60
0.80
1.00
1.20
1.40
1.60
1.80
2.00
TCD
F
12378
PCDF
23478-PC
DF
123478
H
xCD
F
123678
H
xCD
F
234678
H
xCD
F
123789
H
xCD
F
1234678
H
pCD
F
1234789
H
pCD
F
O
C
DF
TCD
D
PCDD
123478
H
xCD
D
123678
H
xCD
D
123789
H
xCD
D
1234678
H
pCD
D
O
C
DD
APGC-MS/MS Consensus PT
Fish meal
0.00
0.50
1.00
1.50
2.00
2.50
TCD
F
12378
PCDF
23478-PC
DF
123478
H
xCD
F
123678
H
xCD
F
234678
H
xCD
F
123789
H
xCD
F
1234678
H
pCD
F
1234789
H
pCD
F
O
C
DF
TCD
D
PCDD
123478
H
xCD
D
123678
H
xCD
D
123789
H
xCD
D
1234678
H
pCD
D
O
C
DD
APGC-MS/MS Consensus QC material
Pork sausage
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
TCD
F
12378
PCDF
23478-PC
DF
123478
H
xCD
F
123678
H
xCD
F
234678
H
xCD
F
123789
H
xCD
F
1234678
H
pCD
F
1234789
H
pCD
F
O
C
DF
TCD
D
PCDD
123478
H
xCD
D
123678
H
xCD
D
123789
H
xCD
D
1234678
H
pCD
D
O
C
DD
APGC-MS/MS Consensus PT
EU NRL comparison between
Consensus PT data and APGC
©2015 Waters Corporation 48
Name Std. Conc RT Area ng/mL 1º Ratio (Pred) 1º Ratio (Actual)
1º Ratio
Flag
Standard 0.05 ng/mL 0.05 6.28 124.2 0.05 1.442 1.403 -2.7
Standard 0.1 ng/mL 0.1 6.27 194.2 0.07 1.442 1.4 -2.9
Standard 0.5 ng/mL 0.5 6.27 1183.4 0.44 1.442 1.442 *
Standard 1 ng/mL 1 6.27 2448.1 0.92 1.442 1.561 8.3
Standard 5 ng/mL 5 6.27 12255 4.59 1.442 1.474 2.2
Standard 10 ng/mL 10 6.27 23042.4 8.63 1.442 1.526 5.8
Standard 20 ng/mL 20 6.27 57394.2 21.50 1.442 1.539 6.7
Standard 50 ng/mL 50 6.27 134669.3 50.46 1.442 1.438 -0.3
QC 1 ng/mL 1 6.26 3058.5 1.14 1.442 1.542 6.9
QC 1 ng/mL 1 6.27 2863.5 1.07 1.442 1.493 3.5
QC 1 ng/mL 1 6.27 2737.6 1.02 1.442 1.47 1.9
QC 1 ng/mL 1 6.27 2808.3 1.05 1.442 1.465 1.6
QC 1 ng/mL 1 6.27 2904.4 1.09 1.442 1.422 -1.4
QC 1 ng/mL 1 6.27 525.5 0.20 1.442 1.499 4.0
QC 1 ng/mL 1 6.27 1945.1 0.73 1.442 1.428 -1.0
QC 1 ng/mL 1 6.26 2038 0.76 1.442 1.371 -4.9
QC 1 ng/mL 1 6.27 2207.5 0.83 1.442 1.404 -2.6
QC 1 ng/mL 1 6.27 1247.4 0.47 1.442 1.384 -4.0
APGC-TQ-S ion ratio stability
* - 0.5 ng/µL standard was determined to be definitive ion ratio
Deviation < 8.5%
©2015 Waters Corporation 49
Summary and Conclusions
 For many food safety and environmental applications (e.g.
POPs, Pesticides) both LC & GC techniques are required
– APGC very easy source exchange
– Robust and easy to use
– FID like chromatography performance (gas flow)
 Commission Regulation 589/2014 permits the use of GC-MS/MS
as an acceptable approach for screening & confirmatory
methods of analysis for dioxins (June 2014)
 APGC is highly selective for many GC methods
– Often use “precursor->product” transitions (MRM) from EI-GC
 Sensitivity of Xevo TQ-S in GC or LC is uncompromised
– Very sensitive in both modes!
©2015 Waters Corporation 50
Acknowledgments and Collaborators
APGC-Xevo-TQ-S
 Rainer Malisch, Alexander Kotz, Helmut Winterhalter, EU-RL for
Dioxins in Food and Feed, Germany
 Prof. Bert van Bavel, Ingrid Ericson, MTM Research Centre,
Örebro University, Sweden
 Juan Vi Sancho, Tania Portolés, Félix Hernández, Universitat
Jaume I, Castellón, Spain
 Wim Broer, Nofalab, The Netherlands
 Richard Fussell, Martin Rose, FERA, UK
 Brock G. Chittim, Wellington Labs, Canada
 Petr Kukučka, Recetox, Czech Republic

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Use of APGC coupled to Tandem Quadrupole Mass Spectrometry for the analysis of Pesticides and Dioxins - Waters Corporation Food Safety

  • 1. ©2015 Waters Corporation 1 Ultra-Trace Level Quantitative Analysis of Food Contaminants using LC and GC coupled to MS
  • 2. ©2015 Waters Corporation 2 Overview  Ultra-trace residue analysis in food – What are the challenges?  Persistent organic pollutants in foods  LC & GC source interfaces & options – Universal source interface – Introduction to the Xevo-TQ-S  Principles of APGC – How does it work? – Multi-residue pesticide analysis (LC & GC amenable) – Commission Regulation 589/2014 – APGC for dioxins  Summary and conclusions
  • 3. ©2015 Waters Corporation 3 Residue & contaminant analysis challenges? Matrix & analyte complexity Sample type & extract preparation Ease of use & implementation Compliance with regulatory performance criteria Validation & AQC requirements
  • 4. ©2015 Waters Corporation 4 Analysis of POPs Requirement for both LC & GC  Stockholm convention – Global agreement to reduce environmental POPs levels – 12 classes of compounds listed – Persistent environmental pollutants  Dioxins: HR-GC-MS (magnetic sector)  BFRs: PBDEs: HR-GC-MS or GC-MS/MS  PFCs: LC-MS/MS  Endocrine disruptors: LC-MS/MS & GC-MS/MS  Nitrosamines: GC-MS/MS  Legacy pesticides: LC-MS/MS & GC-MS/MS O BrBr Br Br Br Br Br Br Br Br Cl Cl O O Cl Cl F F F F F F F F F S O OF F F F F F FF OH Br Br Br Br Br Br Cl Cl O Cl Cl Cl Cl
  • 5. ©2015 Waters Corporation 5 LC and GC Source Interfaces and Options
  • 6. ©2015 Waters Corporation 6 The Universal Source – configurations and options LC
  • 7. ©2015 Waters Corporation 7 APGC Overview  Waters APGC is an optional ion source for Xevo systems that provides a highly sensitive GC-MS, MS/MS capability  Very easy to swap between APGC, UPLC, other ion sources without instrument venting in minutes  APGC ionisation is soft (cf. APCI) and molecular ions are readily detected  Fragmentation can be induced (CID) to provide information for structural elucidation  Xevo tandem quad (Xevo TQ-S) is a powerful tool for routine quantitation coupled to both LC & GC – Capability of using the RADAR for exploratory experiments
  • 8. ©2015 Waters Corporation 8 APGC coupled to Xevo TQ-S - enhanced sensitivity tandem quadrupole- MS
  • 9. ©2015 Waters Corporation 9 Xevo TQ Xevo TQ-S StepWave ScanWave (Collision cell) How did we increase sensitivity? Hexapole (Transfer Optics) 1st Quadrupole (Precursor ion selection) 2nd Quadrupole (Product ion selection) Larger sampling cone aperture = 200x increase in ion flux
  • 10. ©2015 Waters Corporation 10 ElectricField Diffuse Ion Cloud Maximising signal Maximising robustness Designed to deal with problems associated with a larger sampling orifice Compact ion cloud
  • 11. ©2015 Waters Corporation 11 LC and GC on one instrument Sensitive and robust GC LC
  • 12. ©2015 Waters Corporation 12 LC and GC on one instrument Is it possible? ESI
  • 13. ©2015 Waters Corporation 13 LC and GC on one instrument Is it possible? APGC
  • 14. ©2015 Waters Corporation 14 Atmospheric Pressure Gas Chromatography (APGC) How does it work?
  • 15. ©2015 Waters Corporation 15 Universal Source ESI and APGC modifications fitted Sampling cone Electrospray Configuration Vial containing modifier Ion chamber & corona pin APGC Configuration APGC source door Entrance for transfer line
  • 16. ©2015 Waters Corporation 16 Source and Ion Chamber
  • 17. ©2015 Waters Corporation 17 Remove the source housing Plinth mounting – helps ensure correct alignment of the transfer line to the source GC 7890 Exchange between LC and GC No venting required
  • 18. ©2015 Waters Corporation 18 Slide the GC
  • 19. ©2015 Waters Corporation 19 Ready for GC/MS
  • 20. ©2015 Waters Corporation 20 Mass Spec Corona Pin Atmospheric Region Heated Transfer Line Capillary GC Column Ionization Chamber APGC Source Schematic
  • 21. ©2015 Waters Corporation 21 Corona Pin Creates corona discharge at the needle Atmospheric Pressure Source Capillary GC Column Ionization Chamber Ionisation occurs either by charge transfer or proton transfer depending on the conditions in the source Heated Transfer Line Transfer Line GC Make up (sheath) gas N2 250 ml/min together with cone gas supplies nitrogen for the plasma Mass Spectrometer APGC – How it works
  • 22. ©2015 Waters Corporation 22 Mass Analyser GC Oven Corona discharge at needle creates plasma N2 make-up (250ml/min) gas delivered through transfer line interior N2 meets GC eluent flow at transfer line tip Analyte Molecules are ionised after GC elution and directed to the mass analyser APGC – How it works
  • 23. ©2015 Waters Corporation 23 APGC Ionisation Modes & Advantages
  • 24. ©2015 Waters Corporation 24 Mechanism of Ionisation (I) N2 +● N2e- 2e- 2N2 N4 +● M●+ M Corona Pin M●+ M Charge Transfer  “Dry” source conditions  Favored by relatively non-polar compounds
  • 25. ©2015 Waters Corporation 25 Mechanism of Ionisation (II) N2 +● N4 +● H2O H2O+● H2O H3O+● +OH● [M+H]+ M Protonation  Modified source conditions eg. with water or methanol present  Favored by relatively polar compounds Corona Pin
  • 26. ©2015 Waters Corporation 26 Time 2.00 4.00 6.00 8.00 10.00 12.00 14.00 % 0 100 ANAPGC240409TEST009 TOF MS AP+ 278.025 0.02Da 671 8.75 0.01µg/ml BF Std Time 8.00 10.00 12.00 14.00 16.00 18.00 20.00 22.00 % 0 100 CSL_200306_204 TOF MS EI+ 277.018 0.02Da 298 15.98 EI GC 5uL Injection APGC 1uL Injection 298cps EI+ 671cps AP+ Faster run possible due to atm pressure source and higher res MS 15.98 8.75 ~ 10X higher response for APGC Chromatographic Performance Flow rate
  • 27. ©2015 Waters Corporation 27 EI GC/MS compared to APGC-MS Parameter GC/MS APGC Linearity ✔ ✔ Sensitivity ✔ ✔ NIST Library Spectra ✔ ✘ Ease of Use ✘ ✔ Matrix Tolerance ✘ ✔ Low fragmentation spectra ✘ ✔ Access to latest MS innovations ✘ ✔
  • 28. ©2015 Waters Corporation 28 APGC-TQ-S Complete solution for targeted multi-class pesticide residue analysis Circa 60% of pesticides tested in EU require LC-MS & 40% require GC-MS
  • 29. ©2015 Waters Corporation 29 NIST EI Spectrum APGC Spectrum Endosulphan M+. The challenge...
  • 30. ©2015 Waters Corporation 30 Strategy for analysis of LC & GC amenable pesticides
  • 31. ©2015 Waters Corporation 31 SPE for GC-MS Tea Analysis
  • 32. ©2015 Waters Corporation 32 “Difficult” pesticide comparison EI-GC & APGC tR Compounds Molecular formula M EI APGC APGC+H2O M•+ M•+ MH+ MH+ 4.70 Dichlorvos C4H7Cl2O4P 220 +++ +++ 5.97 Mevinphos C7H13O6P 224 ++ + ++ 6.96 Molinate C9H17NOS 187 + +++ +++ 8.00 Dicrotophos C8H16NO5P 237 + ++ ++ +++ 8.24 Monocrotophos C7H14NO5P 223 + ++ ++ +++ 8.95 Terbufos C9H21O2PS3 288 + 9.80 Phosphamidon C10H19ClNO5P 299 + ++ +++ 9.76 Endosulfanether C9H6Cl6O 340 + + ++ ++ 9.94 Chlorpyriphosmethyl C7H7Cl3NO3PS 321 ++ +++ 10.77 Chlorpyriphos C9H11Cl3NO3PS 349 + +++ +++ 10.85 Aldrin C12H8Cl6 362 + + ++ 11.39 Isodrin C12H8Cl6 362 ++ ++ ++ 11.56 Chlorfenvinphos C12H14Cl3O4P 358 ++ +++ 11.56 Oxychlordane C10H4Cl8O 420 + + ++ 11.56 HeptachlorepoxideB C10H5Cl7O 386 + + ++ 12.23 EndosulfanI C9H6Cl6O3S 404 ++ ++ 12.72 Buprofezin C16H23N3OS 305 + ++ +++ +++ 12.73 Dieldrin C12H8Cl6O 378 + ++ ++ ++ 13.10 Endrin C12H8Cl6O 378 ++ ++ ++ 13.36 Ethion C9H22O4P2S4 384 + +++ +++ 14.01 Endosulfansulfate C9H6Cl6O4S 420 ++ ++ 15.63 Azinphosmethyl C10H12N3O3PS2 317 + 15.66 Pyriproxyfen C20H19NO3 321 ++ +++ 16.04 Fenarimol C17H12Cl2N2O 330 + ++ +++ +++ 16.17 Azinphosethyl C12H16N3O3PS2 345 + +, very small peak; ++, clearly identifiable peak (>20%); +++, base peak (or >80%)
  • 33. ©2015 Waters Corporation 33 142 multi-class method for pesticides in fruits & vegetables  QuEChERS including a 10-fold dilution of the final acetonitrile extract  direct injection splitless  [M+H]+ precursor ions for most (90%) compounds  3 SRM transitions /compound Validation  Spiked samples 0.01 and 0.1 mg/kg  Quantification  matrix-matched calibration  Ion ratio tolerances achieved Application Of Gas Chromatography-(Triple Quadrupole) Mass Spectrometry With Atmospheric Pressure Chemical Ionization For The Determination Of Multiclass Pesticides In Fruits And Vegetables, Laura Cherta et al (2013) Journal of Chromatography A (1292) 132-141
  • 34. ©2015 Waters Corporation 34 % Recovery % Frequency % % % 0 20 40 60 80 100 <70 70-110 110-120 >120 -10 10 30 50 70 90 110 130 <70 70-110 110-120 >120 0.01 mg/kg 0.1 mg/kg % Recovery (n=6) 1 pg injected 10 pg injected Performance Data Validation 142 pesticides in three different matrices
  • 35. ©2015 Waters Corporation 35 Authors’ Conclusions…  APCI allows a “universal” soft-ionization for GC-amenable compounds, which provides more selectivity and sensitivity due to the selection of the molecular ion/protonated molecule as precursor ion.  GC-APCI-(QqQ) MS/MS presents good analytical characteristics regarding linearity, precision and limits of detection for determination of target residues in food and environmental samples.  The novel APCI source reveals itself as a good choice to consider in GC-MS/MS for pesticide residue analysis, as well as a suitable alternative to HRMS in the dioxins field
  • 36. ©2015 Waters Corporation 36 Waters pesticide GC method Summary of conditions & performance Compound MRM Quantification Retention time (min) Limit of detection (ng/mL) Correlation Coefficient (R2) Aldrin 363>159 13.4 0.5 0.992 Azinphos-Ethyl 289>261 14.2 0.05 0.993 Azinphos-Methyl 261>125 20.0 0.5 0.990 Buprofezin 306>106 15.9 0.05 0.991 Chlorfenvinphos 359>170 14.3 0.05 0.994 Chlorpyriphos 350>198 13.2 0.1 0.995 Chlorpyriphos-Methyl 322>125 12.1 0.05 0.991 Dichlorvos 221>145 6.3 0.01 0.995 Dicrotophos 238>112 9.6 0.05 0.990 Dieldrin 379>325 16.0 0.1 0.995 Endosulfan I 405>323 15.3 0.1 0.992 Endosulfan-Ether 341>205 18.7 0.01 0.995 Endosulfan-Sulphate 323>217 17.7 0.05 0.992 Endrin 379>243 16.5 0.05 0.997 Ethion 385>143 16.8 0.05 0.996 Fenarimol 331>139 20.7 0.1 0.997 Heptachlor Epox B 387>217 17.7 0.1 0.992 Mevinphos 225>127 7.5 0.05 0.995 Phenthoate 321>135 14.4 0.05 0.993 Phosphamidon 300>127 12.0 0.1 0.993 Wet source conditions used [APGC +H2O], internal standard used Application note reference: 720004776en
  • 37. ©2015 Waters Corporation 37 APGC linearity Azinphos-methyl in strawberry extract, triplicate injection internally standardised R2 = 0.9975
  • 38. ©2015 Waters Corporation 38 APGC – Repeatability in matrix Matrix matched standards at 1 μg/kg n=10
  • 39. ©2015 Waters Corporation 39 Dioxins & furans EU legislation revision for screening & confirmation June 2014
  • 40. ©2015 Waters Corporation 40  Dioxins & dioxin-like compounds (DLC) are by-products of various industrial processes, and are commonly regarded as highly toxic compounds that are environmental and persistent pollutants (POPs)  Analysis must comply with legislative requirements. EPA1613 in USA and (EC) No 152/2009 & 589/2014 in Europe  ‘Gold Standard’ is magnetic sector MS (AutoSpec Premier)  Regulation 589/2014 permits the use of GC-MS/MS for both screening & confirmatory purposes Commission Regulation 589/2014 Screening & confirmatory methods
  • 41. ©2015 Waters Corporation 41 Analytical criteria for use of MS/MS for determination of dioxin-like PCBs in feed & food NEW EU LEGISLATION 02 June 2014
  • 42. ©2015 Waters Corporation 42 APGC application for dioxins & furans  Charge transfer [M+·] precursor ions for all compounds  2 SRM transitions / compound + labelled standards Validation  Analysis of certified reference material  Quantification using commercial standard solutions
  • 43. ©2015 Waters Corporation 43 1368-TCDD min. 2 fg on column 1379-TCDD 1378-TCDD 1478-TCDD 1234-TCDD 2378-TCDD TF-TCDD-MXB; Components and Concentrations (fg/µl, ± 5% in nonane) Component Conc (fg/µl) 1368-TCDD 2 1379-TCDD 5 1378-TCDD 10 1478-TCDD 25 1234-TCDD 50 2378-TCDD 100 13 C-2378-TCDD 5 Sensitivity - TCDD mix
  • 44. ©2015 Waters Corporation 44 1368-TCDD min. 2 fg on column 1379-TCDD 1379-TCDD 1368-TCDD 1378-TCDD 1378-TCDD 1478-TCDD 1478-TCDD 1234-TCDD 1234-TCDD 2378-TCDD 2378-TCDD GC-HRMS GC-MS/MS (QqQ) Sensitivity – comparison to GC-HRMS
  • 45. ©2015 Waters Corporation 45 1613 CSL 10-fold dilution 0.01 ng/mL S/N ≈ 20 Precision - TCDD mix
  • 46. ©2015 Waters Corporation 46 Quantitative performance Linearity over range 10 fg > 40 pg on-column Compound %RSD Calibration RRF Coeff. Of Determination TCDD 3.3 >0.999 TCDF 7.9 >0.999 PCDD 2.8 >0.999 1,2,3,7,8-PCDF 2.8 >0.999 2,3,4,7,8-PCDF 2.1 >0.999 1,2,3,4,7,8-HxCDD 4 >0.999 1,2,3,6,7,8-HxCDD 4.1 >0.999 1,2,3,7,8,9-HxCDD 3.5 >0.999 1,2,3,4,7,8-HxCDF 6.3 >0.999 1,2,3,6,7,8-HxCDF 5 0.999 2,3,4,6,7,8-HxCDF 3 >0.999 1,2,3,7,8,9-HxCDF 8 0.998 1,2,3,4,6,7,8-HpCDD 5.8 >0.999 1,2,3,4,6,7,8-HpCDF 4 >0.999 1,2,3,4,7,8,9-HpCDF 3.3 >0.999 OCDD 1.8 >0.999 OCDF 8.3 0.998 Compound name: TCDD Correlation coefficient: r = 0.999887, r^2 = 0.999774 Calibration curve: 1.02895 * x + -0.00220016 Response type: Internal Std ( Ref 1 ), Area * ( IS Conc. / IS Area ) Curve type: Linear, Origin: Exclude, Weighting: 1/x, Axis trans: None pg/µL -0.0 2.5 5.0 7.5 10.0 12.5 15.0 17.5 20.0 22.5 25.0 27.5 30.0 32.5 35.0 37.5 40.0 Response -0.0 5.0 10.0 15.0 20.0 25.0 30.0 35.0 40.0
  • 47. ©2015 Waters Corporation 47 APGC-TQ-S comparison with HR-GC/MS Fish 0.00 0.20 0.40 0.60 0.80 1.00 1.20 1.40 1.60 1.80 2.00 TCD F 12378 PCDF 23478-PC DF 123478 H xCD F 123678 H xCD F 234678 H xCD F 123789 H xCD F 1234678 H pCD F 1234789 H pCD F O C DF TCD D PCDD 123478 H xCD D 123678 H xCD D 123789 H xCD D 1234678 H pCD D O C DD APGC-MS/MS Consensus PT Fish meal 0.00 0.50 1.00 1.50 2.00 2.50 TCD F 12378 PCDF 23478-PC DF 123478 H xCD F 123678 H xCD F 234678 H xCD F 123789 H xCD F 1234678 H pCD F 1234789 H pCD F O C DF TCD D PCDD 123478 H xCD D 123678 H xCD D 123789 H xCD D 1234678 H pCD D O C DD APGC-MS/MS Consensus QC material Pork sausage 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 TCD F 12378 PCDF 23478-PC DF 123478 H xCD F 123678 H xCD F 234678 H xCD F 123789 H xCD F 1234678 H pCD F 1234789 H pCD F O C DF TCD D PCDD 123478 H xCD D 123678 H xCD D 123789 H xCD D 1234678 H pCD D O C DD APGC-MS/MS Consensus PT EU NRL comparison between Consensus PT data and APGC
  • 48. ©2015 Waters Corporation 48 Name Std. Conc RT Area ng/mL 1º Ratio (Pred) 1º Ratio (Actual) 1º Ratio Flag Standard 0.05 ng/mL 0.05 6.28 124.2 0.05 1.442 1.403 -2.7 Standard 0.1 ng/mL 0.1 6.27 194.2 0.07 1.442 1.4 -2.9 Standard 0.5 ng/mL 0.5 6.27 1183.4 0.44 1.442 1.442 * Standard 1 ng/mL 1 6.27 2448.1 0.92 1.442 1.561 8.3 Standard 5 ng/mL 5 6.27 12255 4.59 1.442 1.474 2.2 Standard 10 ng/mL 10 6.27 23042.4 8.63 1.442 1.526 5.8 Standard 20 ng/mL 20 6.27 57394.2 21.50 1.442 1.539 6.7 Standard 50 ng/mL 50 6.27 134669.3 50.46 1.442 1.438 -0.3 QC 1 ng/mL 1 6.26 3058.5 1.14 1.442 1.542 6.9 QC 1 ng/mL 1 6.27 2863.5 1.07 1.442 1.493 3.5 QC 1 ng/mL 1 6.27 2737.6 1.02 1.442 1.47 1.9 QC 1 ng/mL 1 6.27 2808.3 1.05 1.442 1.465 1.6 QC 1 ng/mL 1 6.27 2904.4 1.09 1.442 1.422 -1.4 QC 1 ng/mL 1 6.27 525.5 0.20 1.442 1.499 4.0 QC 1 ng/mL 1 6.27 1945.1 0.73 1.442 1.428 -1.0 QC 1 ng/mL 1 6.26 2038 0.76 1.442 1.371 -4.9 QC 1 ng/mL 1 6.27 2207.5 0.83 1.442 1.404 -2.6 QC 1 ng/mL 1 6.27 1247.4 0.47 1.442 1.384 -4.0 APGC-TQ-S ion ratio stability * - 0.5 ng/µL standard was determined to be definitive ion ratio Deviation < 8.5%
  • 49. ©2015 Waters Corporation 49 Summary and Conclusions  For many food safety and environmental applications (e.g. POPs, Pesticides) both LC & GC techniques are required – APGC very easy source exchange – Robust and easy to use – FID like chromatography performance (gas flow)  Commission Regulation 589/2014 permits the use of GC-MS/MS as an acceptable approach for screening & confirmatory methods of analysis for dioxins (June 2014)  APGC is highly selective for many GC methods – Often use “precursor->product” transitions (MRM) from EI-GC  Sensitivity of Xevo TQ-S in GC or LC is uncompromised – Very sensitive in both modes!
  • 50. ©2015 Waters Corporation 50 Acknowledgments and Collaborators APGC-Xevo-TQ-S  Rainer Malisch, Alexander Kotz, Helmut Winterhalter, EU-RL for Dioxins in Food and Feed, Germany  Prof. Bert van Bavel, Ingrid Ericson, MTM Research Centre, Örebro University, Sweden  Juan Vi Sancho, Tania Portolés, Félix Hernández, Universitat Jaume I, Castellón, Spain  Wim Broer, Nofalab, The Netherlands  Richard Fussell, Martin Rose, FERA, UK  Brock G. Chittim, Wellington Labs, Canada  Petr Kukučka, Recetox, Czech Republic