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On-Line SPE with the Flexcube/6460 QQQ. Dr. Sheher Bano Mohsin Mass Spectrometry Applications June 11, 2013. Introduction – Why Online SPE? Introducing the Flexcube for Online SPE Sensitivity of the Mass Spectrometers Application Examples - Water Samples - Samples with dirty Matrices. - PowerPoint PPT Presentation
Citation preview
Page 1
On-Line SPE with the Flexcube/6460 QQQ
Dr. Sheher Bano Mohsin Mass Spectrometry ApplicationsJune 11, 2013
04/22/20231
Page 2
22.04.20232
•Introduction – Why Online SPE?
•Introducing the Flexcube for Online SPE
•Sensitivity of the Mass Spectrometers
• Application Examples
- Water Samples
- Samples with dirty Matrices
Page 3
22.04.20233
Solid Phase Extraction (SPE)
Wouldn’t it be great if you could automate SPE while reducing sample and solvent volumes?
Page 4
22.04.20234
Automated on-line SPE 1. Load 500ul-1800 µl water sample on the enrichment cartridge.
2. Valve switch, ‘backflush‘ desorb using HPLC gradient.
3. Separate on the analytical column and collect MRM tranistions on the QQQ.
4. Recondition enrichment cartridge during analysis.
5. Ready for next sample after ~ 20 minutes.
Page 5
22.04.20235
High sensitivity 6460 Triple Quadrupole• Sub-femtogram, on-column sensitivity (1pg reserpine; s/n 2000:1) • Five Orders of Linearity• Fast Pos/Neg switching, 30 millisec• “Dynamic Multiple Reaction Monitoring” for MRMs scheduled by peak
retention times instead of time segments• Triggered MRM for confirmation
Agilent Jet Stream
Page 6
22.04.20236
Agilent MassHunter Software
Instrument ControlReal-time monitoring
Method set-up
Autotune
Qualitative AnalysisChromatographic results
Spectral results
Find compounds
Quantitative AnalysisUser filters
Compound results
Calibration curve
Reporting Easily CustomizableBased on Excel and
XML technology
Page 7
22.04.20237
Agilent Online SPE System
Switching valve with TEC
Quaternary pump
Autosampler
Analytical column for separation
Binary pump for gradient elution
MS/MS
Page 8
22.04.20238
WHAT’S NEW WITH ONLINE SPE?
Flexcube with Built in Valves and a Pump - all Controlled
through Mass Hunter
Page 9
22.04.20239
Agilent Online SPE System
Switching valve with TEC
Quaternary pump
Autosampler
Analytical column for separation
Binary pump for gradient elution
MS/MS
Replace with Flexcube
Page 10
Agilent 1200 Infinity Series Online SPE solution
Solvent selection valve for up to three solvents
Reciprocating single-piston pump for flows up to 4 ml/min (60 bar)
up to two Quick-Change valves, according to application
10
Valves mounted in 1290 Infinity Flexible Cube
Page 11
Online SPE with the Flex Cube
Autosampler with 900uL loop and extension seat capillary
1290 Binary Pump
1290 Autosampler
Column Compartment
6460 QQQ
Flexcube
Autosampler
Page 12
Flex Cube and Autosampler
Single Piston Pump
6 port valve 10 port valve
Autosampler
Page 13
Mass Hunter B 06.00 with Flexcube Control
Page 14
1260 Bin Pump
System with alternating SPE loading:Load sample to SPE1
SPE2
SPE1
Std. ALS 900 µL head
Flex cube pump Column
waste
Load
SPE starter set
Page 15
1260 Bin Pump
System with alternating SPE loading:Elute sample from SPE1 to column / Load sample 2 on SPE2
SPE2
SPE1
Std. ALS 900 µL head
Flex cube Column
waste
Elute
Load
Mass Spec
Page 16
22.04.202316
Application:
Quantitative LC/MS/MS analysis of 24 trace pharmaceuticals and consumer products in water using on-line SPE enrichment.
Tarun Anumol and Shane Snyder University of Arizona
Sheher Mohsin – Agilent Applications Scientist
Page 17
22.04.202317
Compounds AnalyzedCompound Class Compound Class
Atrazine Herbicide PFBS Fluoro-surfactantBisphenol A Plasticizer PFOA Fluoro-surfactant
Caffeine Stimulant PFOS Fluoro-surfactantCarbamazepine Anti-seizure Primidone Anticovulsant
DEET Insect-repellant Simazine HerbicideEstrone Hormone Sulfamethoxazole Antibiotic
Fluoxetine Anti-depressant Atenolol Β-blockerGemfibrozil Anti-cholesterol TCPP Flame-retardantIbuprofen Analgesic Testosterone Hormone
Meprobamate Anti-anxiety Triclocarban Anti-microbialNaproxen Pain-reliever Triclosan Anti-microbialDiltiazem Anti-histamine Trimethoprim Antibiotic
Page 18
22.04.202318
Summary Experimental Methods
1. Collect 5 mL sample and store at 4C for preservation.
2. Filter sample through 0.2 µm filters.
3. Combine 1683 µL of sample (weight using analytical balance for accuracy) with 17 µL of a 10 ppb surrogate standard mix. Vortex for 30 sec.
4. Analyze by UHPLC/MS/MS with the Agilent 1290 LC coupled to an Agilent 6460 Mass Spectrometer LC/MS/MS.
Page 19
Chromatography
04/22/202319
Simultaneous analysis of 24 PPCPs in both ESI+ & ESI- mode.
Injection Volume: 1.5 mL
Cycle time (Extraction + Analysis): 18.5 min
Trace Enrichment Cartridge: PLRP-S, 15 µm
Analytical Column: Poroshell 120 EC, 2.1x50 mm
Page 20
22.04.202320
Analyte MRL Analyte MRL
Atenolol 15 Meprobamate 0.5
Atrazine 5 Naproxen 10
Bisphenol A 10 PFBS 10
Caffeine 0.5 PFOA 10
Carbamazepine 2.5 PFOS 10
DEET 0.1 Primidone 15
Estrone 20 Simazine 1.5
Fluoxetine 10 Sulfamethoxazole 2.5
Gemfibrozil 1.5 TCPP 0.5
Ibuprofen 10 Triclocarban 1
Trimethoprim 5 Triclosan 5
Method Reporting Limits (ng/l)
S/N> 10 (by height) for 3 successive injections
Page 21Confidential21 April 2010
Evaluation of On-line Solid Phase Extraction and Direct Injection-LC/MS/MS for the Analysis of Chemicals on
U.S. EPA’s Contaminant Candidate List 3
Sheher Bano Mohsin
Page 22
Chemicals for LC/MS/MS Evaluation*
•4,4’-methylenedianiline
•3-hydroxycarbofuran
•bensulide
•clethodim
•fenamiphos
•fenamiphos sulfone
•fenamiphos sulfoxide
• methomyl • quinoline• tebuconazole• tebufenozide• thiodicarb
9 CCL3 chemicals 3 CCL3 degradates
*Slide Taken From: Evaluation of On-line Solid Phase Extraction-LC/MS/MS for the Analysis of Chemicals on U.S. EPA’s Contaminant Candidate List 3 - Jody A. Shoemaker and Daniel R. Tettenhorst
Page 23Confidential23 April 2010
Agilent 1200 Infinity Series Online-SPE solution system comprising:G1312B Binary Pump with modular degasserG1329B Standard AutosamplerG4227A Flexible Cube with 2-position/10-port valves, G1316C Thermostatted Column Compartment. 6460 Triple Quadrupole LC/MS with Jet Stream Technology
Online SPE Instrumentation in Schaumburg
Page 24
Configuration showing the plumbing for direct on-column injection and on-line SPE.
Page 25
LC/MS/MS Parameters
Triple Quadruple MS method with Agilent Jet Stream thermal gradient focusing technology:• Gas temperature: 300 °C. Gas flow: 10 L/min.• Nebulizer: 45 psi• Sheath gas temperature: 350 °C. Sheath gas flow: 11 L• Capillary: 4,000 Volt. Nozzle: 0 Volt
Binary Pump:• Solvent A: Water + 0.1% formic acid. • Solvent B: ACN + 0.1% formic acid. Analysis Flow rate: 0.4 mL/min.Column: ZORBAX EclipsePlus C18 3.0x50mm 1.8 μm, 50 °C.Flexible Cube:Valves: 2 of 2-position/10-port Quick-Change valves.Flow rate: 1.0 mL/min. Solvent: A1: 3% MeOH/Water, B1: ACN/IPA/MeOH/Water 1/1/1/1 v/v/v/v.Standard Autosampler fitted with 900 μL metering headAuto-SPE Injection volume: 900 μL using a draw and eject speed of 1,000 μL/min. Direct Injection volume: 90 μL
Page 26
Cmpd Name Prec Ion
Prod Ion
Frag (V)
CE (V) Cell Acc (V)
Ret Time (min)
Ret Window
Polarity
4-4-diaminodiphenylmethane
199.1 106 120 28 3 6.74 1.81 Positive
Bensulide 398 356 100 1 2 11.06 1.11 PositiveBensulide 398 314 100 6 2 11.06 1.11 PositiveBensulide 398 158 100 26 2 11.06 1.11 Positive
Carbofuran-3-hydroxy 238.1 181 110 8 2 8.15 0.94 PositiveCarbofuran-3-hydroxy 238.1 163 110 11 2 8.15 0.94 Positive
Clethodim 360.1 206 120 12 4 11.67 1.15 PositiveClethodim 360.1 166 130 27 4 11.67 1.15 Positive
Fenamiphos 304.1 234 150 15 3 10.28 1.03 PositiveFenamiphos 304.1 217 150 23 3 10.28 1.03 PositiveFenamiphos 304.1 202 150 31 3 10.28 1.03 Positive
Fenamiphos-sulfone 336.1 308 130 15 3 9.13 0.91 PositiveFenamiphos-sulfone 336.1 266 130 18 3 9.13 0.91 PositiveFenamiphos-sulfone 336.1 188 130 24 3 9.13 0.91 Positive
Fenamiphos-sulfoxide 320.1 292 150 9 3 8.64 0.99 PositiveFenamiphos-sulfoxide 320.1 233 150 23 3 8.64 0.99 PositiveFenamiphos-sulfoxide 320.1 171 150 18 3 8.64 0.99 Positive
Methomyl 163 107 170 17 2 8.15 1.14 PositiveMethomyl 163 95 170 17 2 8.15 1.14 PositiveQuinoline 130 103 120 30 3 6.97 1.81 PositiveQuinoline 130 77 120 30 3 6.97 1.81 Positive
Tebuconazole 308.1 125 130 42 3 10.49 1.05 PositiveTebuconazole 308.1 70 130 23 3 10.49 1.05 PositiveTebufenozide 353.2 297 85 1 3 10.85 1.09 PositiveTebufenozide 353.2 133 85 15 3 10.85 1.09 Positive
Thiodicarb 355 163 80 2 3 9.17 1.28 PositiveThiodicarb 355 108 80 14 3 9.17 1.28 PositiveThiodicarb 355 88 80 17 3 9.17 1.28 Positive
Dynam
ic MR
M Transitions
Page 27
5x10
00.10.20.30.40.50.60.70.80.9
11.11.21.31.41.51.6
+ESI TIC MRM CF=0.000 DF=0.000 (** -> **) 10ppt-r002.d 1 1
Counts vs. Acquisition Time (min)6 6.5 7 7.5 8 8.5 9 9.5 10 10.5 11 11.5 12
Superimposed chromatograms Showing Reproducibility of Retention time as well as Area Counts for two runs Alternating Between two Different SPE Cartridges. The calibration standard used has a concentration of 10 ppt (ng/L) each for all 12 compounds with quantifier and qualifier ions. Each run alternates between two different SPE cartridges.
Page 28
Mix at 1 ppt
3x10
00.10.20.30.40.50.60.70.80.9
11.1
+ESI MRM Frag=100.0V CF=0.000 DF=0.000 [email protected] (398.0000 -> 356.0000) 1ppt-r001.d 11.0481 1
Counts vs. Acquisition Time (min)6 6.2 6.4 6.6 6.8 7 7.2 7.4 7.6 7.8 8 8.2 8.4 8.6 8.8 9 9.2 9.4 9.6 9.8 10 10.2 10.4 10.6 10.8 11 11.2 11.4 11.6 11.8 12
Fenomiphos Sulfoxide
Fenomiphos Sulfone
Tebufenozide
Thiodicarb
Clethodim
Bensulide
Tebuconazole
Fenomiphos
Carbofuran-3-Hydroxy
Methomyl
Quinoline
4,4-diaminodiphenyl methane
Page 29
Mix at 0.1 ppt
2x10
00.5
11.5
22.5
33.5
44.5
55.5
66.5
+ESI MRM Frag=100.0V CF=0.000 DF=0.000 [email protected] (398.0000 -> 356.0000) 0-1ppt-r002.d
11.042
1 1
Counts vs. Acquisition Time (min)6 6.2 6.4 6.6 6.8 7 7.2 7.4 7.6 7.8 8 8.2 8.4 8.6 8.8 9 9.2 9.4 9.6 9.8 10 10.2 10.4 10.6 10.8 11 11.2 11.4 11.6 11.8 12
Page 30
1 ppt and 0.1 ppt
3x10
00.20.40.60.8
11.21.41.61.8
22.22.42.6
+ESI MRM Frag=130.0V CF=0.000 DF=0.000 [email protected] (336.1000 -> 266.0000) 0-1ppt-r002.d
9.123
1
Counts vs. Acquisition Time (min)7.4 7.6 7.8 8 8.2 8.4 8.6 8.8 9 9.2 9.4 9.6 9.8 10 10.2 10.4 10.6 10.8 11 11.2 11.4 11.6 11.8 12
1 ppt
0.1 ppt 1 ppt
0.1 ppt
1ppt
0.1 ppt
1 ppt
0.1 ppt
1 ppt
0.1 ppt
Page 31
Direct Injection and online-SPESame amount on column
4x10
0
2
4
6
8
+ESI TIC MRM CF=0.000 DF=0.000 (** -> **) 50-direct-r002b.d 1 1
4x10
0
2
4
6
8
+ESI TIC MRM CF=0.000 DF=0.000 (** -> **) 5ppt-r002.d 1 1
Counts vs. Acquisition Time (min)1.5 2 2.5 3 3.5 4 4.5 5 5.5 6 6.5 7 7.5 8 8.5 9 9.5 10 10.5 11 11.5 12
Direct Injection
Online SPE
Page 32
Fenomiphos Sulfoxide
2x10
0.5
1
1.5
2
2.5
3
3.5
4
+ESI MRM Frag=150.0V CF=0.000 DF=0.000 [email protected] (320.1000 -> 171.0000) 0-1ppt-r001.d Noise (RMS) = 14.76; SNR (8.635min) = 8.2
1218.635
Counts vs. Acquisition Time (min)7.8 8 8.2 8.4 8.6 8.8 9 9.2 9.4 9.6 9.8 10 10.2 10.4 10.6
0.1 ppt
0.5 ppt
1.0 ppt
Page 33
Fenomiphos Sulfoxide0.1 ppt to 100 ppt
On-line SPE
Fenamiphos-sulfoxide - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 5x10
-0.250
0.250.5
0.751
1.251.5
1.752
2.252.5
2.753
3.253.5
3.754
4.254.5
4.75
y = 4783.281270 * x - 1547.513777R^2 = 0.99976373Type:Linear, Origin:Ignore, Weight:None
Page 34
Fenomiphos Sulfone
2x10
0.5
1
1.5
2
2.5
3
3.5
+ESI MRM Frag=130.0V CF=0.000 DF=0.000 [email protected] (336.1000 -> 188.0000) 0-1ppt-r001.d Noise (RMS) = 17.73; SNR (9.134min) = 7.9
1399.134
Counts vs. Acquisition Time (min)7.8 8 8.2 8.4 8.6 8.8 9 9.2 9.4 9.6 9.8 10 10.2 10.4 10.6
1 ppt
0.5 ppt
0.1 ppt
Page 35
Fenomiphos Sulfone 0.1 ppt to 100 ppt
Online -SPE
Fenamiphos-sulfone - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 5x10
-0.5-0.25
00.250.5
0.751
1.251.5
1.752
2.252.5
2.753
3.253.5
3.754
4.254.5
4.755
5.25
y = 5253.702203 * x - 554.970972R^2 = 0.99622328Type:Linear, Origin:Ignore, Weight:1/x
Page 36
Tebufenozide
3x10
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
+ESI MRM Frag=85.0V CF=0.000 DF=0.000 [email protected] (353.2000 -> 133.0000) 0-1ppt-r001.d Noise (RMS) = 40.87; SNR (10.848min) = 9.4
10.848
Counts vs. Acquisition Time (min)9.2 9.4 9.6 9.8 10 10.2 10.4 10.6 10.8 11 11.2 11.4 11.6 11.8
1 ppt
0.5 ppt
0.1 ppt
Page 37
Tebufenozide
Online SPE
Tebufenozide - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 6x10
-0.1
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
1.1
1.2
1.3
1.4
1.5
1.6
y = 16113.938761 * x - 3077.721444R^2 = 0.99982638Type:Linear, Origin:Ignore, Weight:None
Page 38
Thiodicarb
2x10
0.5
1
1.5
2
2.5
3
3.5
+ESI MRM Frag=80.0V CF=0.000 DF=0.000 [email protected] (355.0000 -> 108.0000) 0-1ppt-r001.d Noise (RMS) = 7.31; SNR (9.167min) = 9.0
9.167
Counts vs. Acquisition Time (min)7.4 7.6 7.8 8 8.2 8.4 8.6 8.8 9 9.2 9.4 9.6 9.8 10
Page 39
Thiodicarb
Online SPE
Thiodicarb - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 6x10
-0.050
0.050.1
0.150.2
0.250.3
0.350.4
0.450.5
0.550.6
0.650.7
0.750.8
0.850.9
0.951
y = 9712.750738 * x - 371.407180R^2 = 0.99900590Type:Linear, Origin:Ignore, Weight:None
Page 40
Clethodim
2x10
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
+ESI MRM Frag=120.0V CF=0.000 DF=0.000 [email protected] (360.1000 -> 206.0000) 0-1ppt-r001.d Noise (RMS) = 4.22; SNR (11.678min) = 7.0
* 11.678
1
Counts vs. Acquisition Time (min)9.8 10 10.2 10.4 10.6 10.8 11 11.2 11.4 11.6 11.8 12 12.2 12.4 12.6
Page 41
Clethodim0.1 ppt to 100 ppt
Online-SPE
Clethodim - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 4x10
-0.5
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
5.5
6
6.5
7y = 671.580771 * x - 96.141931R^2 = 0.99912930Type:Linear, Origin:Ignore, Weight:None
Page 42
Bensulide
2x10
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
+ESI MRM Frag=100.0V CF=0.000 DF=0.000 [email protected] (398.0000 -> 158.0000) 0-1ppt-r001.d Noise (RMS) = 8.95; SNR (11.064min) = 10.3
11.064
1
Counts vs. Acquisition Time (min)9.8 10 10.2 10.4 10.6 10.8 11 11.2 11.4 11.6 11.8 12 12.2 12.4 12.6
1 ppt
0.5 ppt
0.1 ppt
Page 43
Bensulide
Online SPE
Bensulide - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 5x10
-0.5
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
5.5
6y = 5847.762254 * x - 167.472128R^2 = 0.99942301Type:Linear, Origin:Ignore, Weight:None
Page 44
Tebuconazole
4x10
0
0.2
0.4
0.6
0.8
1
1.2
1.4
+ESI MRM Frag=130.0V CF=0.000 DF=0.000 [email protected] (308.1000 -> 70.0000) 0-1ppt-r001.d Noise (RMS) = 10.64; SNR (10.484min) = 427.1
10.484
Counts vs. Acquisition Time (min)10 10.1 10.2 10.3 10.4 10.5 10.6 10.7 10.8 10.9 11
1 ppt
0.5 ppt
0.1 ppt
Page 45
Tebuconazole0.1 ppt to 100 ppt
Online SPE
Tebuconazole - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 6x10
-0.2
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
2.2
2.4
2.6
2.8
3y = 29206.177838 * x + 9683.405016R^2 = 0.99961760Type:Linear, Origin:Ignore, Weight:None
Page 46
Fenomiphos
3x10
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
+ESI MRM Frag=150.0V CF=0.000 DF=0.000 [email protected] (304.1000 -> 202.0000) 0-1ppt-r001.d Noise (RMS) = 10.62; SNR (10.278min) = 31.2
10.278
Counts vs. Acquisition Time (min)9.2 9.4 9.6 9.8 10 10.2 10.4 10.6 10.8 11 11.2
1 ppt
0.5 ppt
0.1 ppt
Page 47
Fenomiphos
Online SPE
Fenamiphos - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 6x10
-0.2
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
2.2
2.4
y = 24586.927512 * x - 1805.458763R^2 = 0.99986119Type:Linear, Origin:Ignore, Weight:None
Page 48
Carbofuran-3-Hydroxy
3x10
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
+ESI MRM Frag=110.0V CF=0.000 DF=0.000 [email protected] (238.1000 -> 163.0000) 0-1ppt-r001.d Noise (RMS) = 34.21; SNR (8.143min) = 34.4
8.143
1
Counts vs. Acquisition Time (min)3.5 4 4.5 5 5.5 6 6.5 7 7.5 8 8.5
1 ppt
0.5 ppt
0.1 ppt
Page 49
Carbofuran-3-Hydroxy
Online SPE
Carbofuran-3-hydroxy - 7 Levels, 7 Levels Used, 14 Points, 14 Points Used, 0 QCs
Concentration (pg/ml)-5 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105
Resp
onse
s 6x10
-0.1
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
1.1
1.2
1.3
1.4
y = 14014.214494 * x + 12281.460374R^2 = 0.99789149Type:Linear, Origin:Ignore, Weight:None
Page 50
Quinoline
4x10
0
1
2
3
4
5
6
7
+ESI MRM Frag=120.0V CF=0.000 DF=0.000 [email protected] (130.0000 -> 77.0000) 0-1ppt-r001.d Noise (RMS) = 103.21; SNR (6.972min) = 594.0
6.972
1
Counts vs. Acquisition Time (min)4 4.5 5 5.5 6 6.5 7 7.5 8 8.5
1 ppt
0.5 and 0.1 ppt
Page 51
Quinoline0.1 to 1000 ppt
Online SPE
Quinoline - 10 Levels, 10 Levels Used, 18 Points, 18 Points Used, 0 QCs
Concentration (pg/ml)0 100 200 300 400 500 600 700 800 900 1000
Resp
onse
s 6x10
-0.4-0.2
00.20.40.60.8
11.21.41.61.8
22.22.42.62.8
33.23.43.63.8
44.24.4
y = 4212.447667 * x + 37135.461218R^2 = 0.96037929Type:Linear, Origin:Ignore, Weight:1/x
Page 52
Water Samples Analysis
Water samples from a lake-fed municipal water supply (tap), residential well (ground), a suburban collection basin (WestLake) and a flood control reservoir (Spring Creek) were analyzed. Notably, both WestLake and Spring Creek are in the drainage basin of nearby public and private golf courses.
Samples were filtered with 0.45 um disk filters prior to analysis.
Page 53
Tebuconazole in Water
5x10
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
+ESI TIC MRM CF=0.000 DF=0.000 (** -> **) filtered Westlake1.d
Counts vs. Acquisition Time (min)6.5 7 7.5 8 8.5 9 9.5 10 10.5 11
Spring Creek 50 ppt
WestLake 37 ppt
Ground 0.9 ppt
Tap 0.004 ppt
Page 54
Lake Water and Ground water
5x10
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
+ESI MRM Frag=130.0V CF=0.000 DF=0.000 [email protected] (308.1000 -> 70.0000) filtered Westlake1.d 1
Counts vs. Acquisition Time (min)8 8.5 9 9.5 10 10.5 11 11.5 12
Ground Water
Lake Water
Amount ~ 50 ppt
Results are based on the average of duplicate analyses, for the one quantifier transition (308.1 to 70.0) and one qualifier transition (308.1 to 125.0). Tebuconazole is used as a fungicide for turf control. Both WestLake and Spring Creek are in the drainage basin of nearby public and private golf courses.
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Compound Name Level (ppt) Signal to Noise (S/N)
Nominal LOQ @ 10:1 S/N
4-4-diaminodiphenylmethane
0.1 25 0.04
Bensulide 0.1 10.3 0.1Carbofuran-3-hydroxy 0.1 34.4 0.03
Clethodim 0.1 7 0.15Fenamiphos 0.1 301.2 0.005
Fenamiphos-sulfone 0.1 7.9 0.15Fenamiphos-sulfoxide 0.1 8.2 0.15
Methomyl 0.1 8.3 0.15Quinoline* 0.1 500 0.002
Tebuconazole 0.1 427 0.0025Tebufenozide 0.1 9.4 0.15
Thiodicarb 0.1 9 0.15* uncertainty due to unresolved carryover
Performance data for all compounds present in the study based on the calculated signal to noise at 0.1 ppt and assuming an LOQ at approximately 10: 1 signal-to-noise. The signal to noise calculation is based on peak area and noise is RMS x 3.
Page 56Confidential56
Trace level analysis of herbicides in drinking and surface water by online-SPE LC/triple quadruploe MS to the lower ppt rangeEdgar Naegele, Agilent Technologies R&D and Marketing GmbH & Co. KG, Waldbronn, Germany
April 2010
Page 57Confidential57 April 2010
MRM and dynamic MRM MS method
Page 58Confidential58 April 2010
Chromatograms of a calibration standard with a concentration of 100 ppt (ng/L) each for all 28 pesticides measured by the final SPE-LC dynamic MRM method with quantifier and
qualifier ion.
Page 59Confidential59 April 2010
Water samples from a tap, Rhine river, and a spring spiked with 25 ppt of all 28 pesticides. The retention time window from 14.5 minutes to 19.1 minutes is shown. The table shows the average measured concentrations of all pesticides (n=12) within the retention time window dependent on the sources of water together with precision RSD and accuracy.
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Conclusions
We have demonstrated an integrated, cost effective scheme to do on-line SPE coupled to LC/MS/MS. The technical barriers and potential technology transfer problems associated with traditional online SPE system have been avoided.The direct coupling of the SPE cartridges (PLRP-S, 2.1x12.5mm, 15-20um) to the LC/MS/MS system was done through the integrated valves. The use of Dynamic MRM enables complex mixtures to be efficiently analyzed.
We have demonstrated excellent performance with challenging contaminants on the contaminant list. LOQ for all components was nominally 1 ppt or lower.
Results for real samples, including ground water, lake and flood control reservoir, the latter two obviously containing visible swimming organisms, produced measurable tebuconazole results.
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Agilent 1200 Infinity Series Online SPE solution
61
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• Boost Performanceenrichment of analytes and matrix removal for utmost sensitivity
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For online sample preparation, upgrade your system with Agilent 1290 Infinity Flexible Cube featuring
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Page 62Confidential62
Journal of Chromatography A, 1286 (2013) 166– 174Quantitative analysis of naphthenic acids in water by liquid chromatography–accurate mass time-of-flight mass spectrometry
Ralph Hindle, Matthew Noesthedena, Kerry Perub, John Headley
Vogon Laboratory Services Ltd., Unit 4, 34 Griffin Industrial Pt., Cochrane, Alberta T4C 0A3, Canada
Water Science & Technology Directorate, Environment Canada, 11 Innovation Blvd., Saskatoon, SK S7N 3H5, Canada
April 2010