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User Benefits Application News The optimized procedure for pretreatment and LC-MS/MS analytical conditions enable accurate quantification of thirty major PFASs targeted by AOAC SMPR from 0.1 µg/kg. The method allows the initiation of PFASs analysis in food. Analysis of Per- and Polyfluoroalkyl Substances (PFAS) using Triple Quadrupole Mass Spectrometer Part 1 -Fish Fillet- Nozomi Maeshima High Performance Liquid chromatograph Mass Spectrometer LCMS-8060NX Introduction Per- and Polyfluoroalkyl Substances (PFASs) are a collective name for more than four thousand organofluorine compounds. Perfluorooctane sulfonic acid (PFOS) and perfluorooctanoic acid (PFOA) are representative compounds of PFAS. They are used in a wide range of applications, such as fire retardants, food packaging materials, and non-stick coatings, due to their water- repellent, oil-repellent, heat-resistant, and chemical-resistant properties. Due to their structural stability, PFAS widely remains in the environment. There are concerns about health risks caused by human ingestion of fish that have ingested seawater, river water, or feed contaminated with PFAS. Therefore, quantitative assessment of PFAS levels in fish should be important. This application news introduces a quantitative analysis of PFAS in tuna fillets with LC-MS/MS. Thirty principal PFASs targeted by AOAC INTERNATIONAL, a North American organization that standardizes food testing methods and verifies analytical methods, were analyzed using newly created method, which was investigated from the pretreatment procedure then validated by recovery test. By reducing losses during the pretreatment and optimizing the analytical conditions, good recovery rates were obtained for all compounds. Sample and pretreatment As standards and internal standards (ISTDs), L-PFUdS, L-PFTrDS, L-PFDoS, and 10:2 FTS and two standard mixtures of PFAC30PAR and MPFAC-HIF-ES were purchased from Wellington Laboratories. Tuna fillet was purchased at a local grocery store, and frozen and crushed with dry ice using a freeze grinder FST-4000 (AiSTI SCIENCE). The samples were left in a freezer overnight, and the dry ice was removed before the pretreatment. Extraction was performed using the QuEChERS method as a reference. The procedure is shown in Fig. 2. 10 g of frozen crushed sample was weighed, added ISTDs and 10 mL of acetonitrile, and shaken vigorously for 1 min. One packet of QuEChERS extraction salt (Restek, P/N: 25849) was added and immediately shaken vigorously by hand for 1 min then centrifuged at 4,000 rpm for 5 min at room temperature. Acetonitrile layer was collected then diluted 5-fold with water and used as extract. EVOLUTE PFAS (Biotage, P/N: 614-0015-CP, 150 mg/6 mL) and a positive pressure manifold PRESSURE+ (Biotage) were used for solid-phase extraction. The procedure is shown in Fig. 3. After conditioning with 5 mL of 28% ammonium hydroxide/ methanol (1:100, v/v) and 5 mL of formic acid/methanol (1:1000, v/v), 40 mL of extraction solution (equivalent to 8 g of fish sample) was loaded. Following washing with 5 mL of water and 5 mL of formic acid/methanol/water (1:400:600, v/v/v), the analytes were eluted with 5 mL of 28% ammonium hydroxide/methanol/water (1:90:10, v/v/v). The eluate was taken 500 µL and mixed with 2 µL of formic acid, then analyzed by LC-MS/MS. Table 1 Analytical conditions of LC-MS/MS [HPLC conditions] Nexera X3 Column : Shim-pack Scepter TM C18-120 (100 mm x 2.1 mm I.D., 3 µm) *1 Delay column : Shim-pack Scepter C18-120 (50 mm x 2.1 mm I.D., 3 µm) *2 Mobile phase A : 2 mmol/L Ammonium Acetate in Acetonitrile/Water (5:95, v/v) Mobile phase B : Acetonitrile Flow rate : 0.3 mL/min (0.6 mL/min only between 10.01-12 min) Gradient program : B conc. 20% (0 min) → 100% (10-12 min) → 20% (12.01-15 min) The flow was loaded onto the mass spectrometer between 1 to 9.6 min using a flow switching valve. Column temp. : 40˚C Injection volume : 5 µL [MS conditions] LCMS-8060NX Ionization : ESI, Negative mode Nebulizing gas : 2 L/min Heating gas : 10 L/min Drying gas : 10 L/min DL temp. : 200˚C Interface temp. : 250˚C Heat block temp. : 400˚C Probe position : +2 mm *1 227-31014-05 *2 227-31014-03 Analytical conditions Analysis was performed using a triple quadrupole mass spectrometer LCMS-8060NX equipped with an ultra-high performance liquid chromatograph Nexera TM X3 UHPLC (Fig. 1). The analytical conditions are shown in Table 1. To prevent interference caused by PFAS contamination from analytical equipment, solvents and glassware, a delay column was installed between mixer and autosampler using SUS piping (300 mm x 0.3 mm I.D., P/N: 228-69955-41). The delay column increased the elution time of PFAS derived from the LC system, allowing it to be separated from the PFAS in the sample. PP vials (Shimadzu GLC, P/N: GLC-IVS-100) confirmed to have no detectable PFAS were observed. Fig. 1 Nexera TM X3 and LCMS-8060NX
Application News Fig. 2 Extraction procedure 5 mL of 28% Ammonia solution/Methanol = 1:100(v/v) 5 mL of Formic acid/Water = 1:1000(v/v) Conditioning Load 40 mL of Extract solution (equivalent to 8 g of fish sample) Wash 5 mL of Water 5 mL of Formic acid/Methanol/Water = 1:400:600(v/v/v) Elute 5 mL of 28% Ammonia solution/Methanol/Water = 1:90:10(v/v/v) LC-MS analysis Add 2 µL of Formic acid to the eluate of 500 µL Inject 5 µL of the resulting mixture SPE cartridge (150 mg/6 mL) EVOLUTE PFAS (Biotage) Fig. 3 Purification procedure Fig. 4 MRM chromatograms of spiked PFAS in tuna fillet samples 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 min 0.0 0.5 1.0 1.5 2.0 (x100,000) 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 min 0.0 0.5 1.0 1.5 2.0 (x1,000,000) 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 min 0.0 2.5 5.0 7.5 (x1,000,000) 10 µL of Internal standard 10 mL of Acetonitrile Shaken for 1 minute Q-sep QuEChERS Extraction Salt Shaken for 1 minute by hand Centrifugation at 4,000 rpm for 5 minutes 10 g of Fish (frozen-ground) Acetonitrile layer Extract solution 5-fold diluting with water Spiked conc. 0.1 µg/kg Spiked conc. 1 µg/kg Spiked conc. 5 µg/kg Conc.Ratio 0 1 2 3 4 5 Area Ratio 0 1 2 3 4 5 6 7 8 PFOS y = 1.705196x + 0.03757239 R² = 0.9977369 R = 0.9988678 Curve Fit: Default (Linear) Weighting: Default (1/A^2) Zero: Default (Not Forced) Conc.Ratio 0 1 2 3 4 5 Area Ratio 0 1 2 3 4 5 6 7 8 9 PFOA y = 1.790071x + 0.007222275 R² = 0.9989693 R = 0.9994845 Curve Fit: Default (Linear) Weighting: Default (1/A^2) Zero: Default (Not Forced) Conc.Ratio 0 1 2 3 4 5 Area Ratio 0 5 10 15 20 25 PFNA y = 5.436417x + 0.01783226 R² = 0.9975520 R = 0.9987753 Curve Fit: Default (Linear) Weighting: Default (1/A^2) Zero: Default (Not Forced) Conc.Ratio 0 1 2 3 4 5 Area Ratio 0 1 2 3 4 5 6 7 PFHxS y = 1.608597x - 0.001575762 R² = 0.9901779 R = 0.9950768 Curve Fit: Default (Linear) Weighting: Default (1/A^2) Zero: Default (Not Forced) PFOS PFOA PFNA PFHxS Fig. 5 Calibration curve at spiked concentrations ranging from 0.05 to 5 µg/kg MRM chromatograms and calibration curves MRM chromatograms of simultaneous analysis for thirty PFAS are shown in Fig. 4. All compounds were eluted within 8 min in great separation. Taurodeoxycholic acid (TDCA), taurocheno- deoxycholic acid (TCDCA), and tauroursodeoxycholic acid (TUDCA), which were concerned to affect the MRM transitions of PFOS, were confirmed to be sufficiently separated from PFOS (data not shown). Calibration curves for representative compounds are shown in Fig. 5. The standard compounds spiked into frozen crushed tuna fillets along with ISTD were subjected to the pretreatment procedure, and a calibration curve was created in the range from 0.05 to 5 μg/kg for all target compounds. The coefficients of determination (R²) were 0.98 for 10:2 FTS, and higher than 0.99 for the other compounds, indicating good linearity was achieved. The concentration of the solution in the vial ranged from 0.07 to 7 ng/mL.
Application News www.shimadzu.com/an/ Shimadzu Corporation © Shimadzu Corporation, 2024 For Research Use Only. Not for use in diagnostic procedures. This publication may contain references to products that are not available in your country. Please contact us to check the availability of these products in your country. The content of this publication shall not be reproduced, altered or sold for any commercial purpose without the written approval of Shimadzu. See http://www.shimadzu.com/about/trademarks/index.html for details. Third party trademarks and trade names may be used in this publication to refer to either the entities or their products/services, whether or not they are used with trademark symbol “TM” or “”. Shimadzu disclaims any proprietary interest in trademarks and trade names other than its own. The information contained herein is provided to you "as is" without warranty of any kind including without limitation warranties as to its accuracy or completeness. Shimadzu does not assume any responsibility or liability for any damage, whether direct or indirect, relating to the use of this publication. This publication is based upon the information available to Shimadzu on or before the date of publication, and subject to change without notice. First Edition: Oct. 2024 01-00750-EN Nexera and Shim-pack Scepter are trademarks of Shimadzu Corporation or its affiliated companies in Japan and/or other countries. Recovery test Recovery tests were conducted at 0.1, 1, and 5 µg/kg, and the recovery rates and repeatability were evaluated. The results are shown in Fig. 6. The procedure was performed from pretreatment in triplicate, and the area values were corrected using the combination of the standard substances and ISTDs shown in the table 2, with quantification carried out using a matrix calibration curve. According to the requirements of AOAC SMPR, PFOS, PFOA, PFNA, and PFHxS are specified to have limit of quantification (LOQ) of 0.1 µg/kg or less, recovery rate within 80-120%, and repeatability 10% or less. For other compounds, 0 5 10 15 20 0 20 40 60 80 100 120 %RSD (%) Recovery rate (%) Recovery rate (%) %RSD (%) 0 5 10 15 20 0 20 40 60 80 100 120 %RSD (%) Recovery rate (%) recovery rate (%) %RSD (%) 0 5 10 15 20 0 20 40 60 80 100 120 %RSD (%) Recovery rate (%) recovery rate (%) %RSD (%) Spiked conc. 0.1 µg/kg Spiked conc. 1 µg/kg Spiked conc. 5 µg/kg Fig. 6 Recovery rate and repeatability of QC samples (n = 3) Compound LOQ (µg/kg) Recovery (%) Repeatability (%) PFOS ≦0.1 80-120 ≦20 PFOA ≦0.1 80-120 ≦20 PFNA ≦0.1 80-120 ≦20 PFHxS ≦0.1 80-120 ≦20 Other PFAS ≦1.0 65-135 ≦25 Table 3 Criteria from AOAC SMPR Compound ISTD PFBA 13 C4-PFBA PFPeA 13 C5-PFPeA PFHxA 13 C5-PFHxA PFHpA 13 C4-PFHpA PFOA 13 C8-PFOA PFNA 13 C9-PFNA PFDA 13 C6-PFDA PFUnA 13 C7-PFUnA PFDOA 13 C7-PFUnA PFTrDA 13 C8-PFOSA PFTeDA 13 C2-PFTeDA PFBS 13 C3-PFBS PFPeS 13 C4-PFHpA PFHxS 13 C3-PFHxS PFHpS 13 C6-PFDA Compound ISTD PFOS 13 C8-PFOS PFNS 13 C7-PFUnA PFDS 13 C2-PFDoA PFUnDS 13 C8-PFOSA PFDOS 13 C2-PFTeDA PFTrDS 13 C2-PFTeDA PFOSA 13 C8-PFOSA 9Cl-PF3ONS 13 C8-PFOS 11Cl-PF3OUdS 13 C3-HFPO-DA HFPO-DA 13 C3-HFPO-DA DONA 13 C4-PFHpA 4:2 FTS 13 C2-4:2 FTS 6:2 FTS 13 C2-6:2 FTS 8:2 FTS 13 C2-8:2 FTS 10:2 FTS 13 C2-8:2 FTS Table 2 Combination of compound and ISTD compounds, LOQ of 1.0 µg/kg or less, recovery rate within 65- 135%, and repeatability of 25% or less (Table 3). For all compounds, recovery rate within 81.6-114.1% and repeatability below 17.1% were achieved at spiked concentrations of 0.1, 1, and 5 µg/kg. Conclusion This application news described a quantitative analysis of thirty PFAS targeted by AOAC INTERNATIONAL in tuna fillet. The analysis was performed using a quadrupole mass spectrometer LCMS-8060NX equipped with ultra-high performance liquid chromatograph Nexera X3 UHPLC system. Shim-pack Scepter, which provides good separation and peak shape, was used as the column. A spiked recovery test were conducted, and all compounds showed recovery rate within 80-120% and repeatability below 20% at spiked concentrations of 0.1, 1, 5 µg/kg. In particular, recovery rates of PFOS, PFOA, PFNA, and PFHxS were within 95.5-108.4% at all spiked concentrations. Using optimized pretreatment and analytical methods, accurate quantitation is possible from 0.1 µg/kg. Reference 1) AOAC SMPR®2023.003
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