EU Priority PAH Analysis in Pumpkin Seed Oil Using Bond Elut EMR Lipid Cleanup by GC/MS/MS

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Application Note Food Testing & Agriculture EU Priority PAH Analysis in Pumpkin Seed Oil Using Bond Elut EMR Lipid Cleanup by GC/MS/MS Authors Thorsten Bernsmann Chemisches und Veterinäruntersuchungsamt Münsterland-Emscher-Lippe (CVUA-MEL), AöR Münster, Germany Diana Wong, Limian Zhao, Bruce Quimby, and Joerg Riener Agilent Technologies, Inc. Abstract European Union (EU) priority polycyclic aromatic hydrocarbons (PAHs) were analyzed in pumpkin seed oil using a liquid-liquid extraction, followed by Bond Elut EMR Lipid (EMR Lipid) and PSA/C8/MgSO 4 dspe (PSA/C8/MgSO 4 ) cleanup. PAHs were quantified using a gas chromatography triple quadrupole mass spectrometer (GC/MS/MS) equipped with an Agilent JetClean self-cleaning ion source (JetClean) and backflush (BF). The JetClean prevents PAH deposition in the source by introducing a low flow of hydrogen during analysis. Column lifetime is improved with the use of postrun midcolumn BF. High collision energy ( ev) was used to remove matrix interference during multiple reaction monitoring (MRM) analysis of PAHs. PAH recoveries were within the EU regulation limits of to % for the mideluting PAHs at prespiked levels of,, and ng/g. Heavy PAHs met the EU Regulation limits only at the ng/g prespiked level. RSD recoveries were within EU regulation limits of below % for all PAH investigated except for benzo(a)pyrene prespiked at ng/g with an RSD of %. Precision and accuracy analysis were used to verify method quantitation with accuracy of ± % and RSD < % at all three prespiked levels. Limit of quantitation (LOQ) was ng/g for all PAHs investigated except for cyclopenta(cd)pyrene and -methylchrysene at ng/g. Linear calibration was observed with a R >.99.

Introduction PAHs are a group of organic compounds composed of two or more aromatic rings that contain only carbon and hydrogen. The formation of PAHs occurs during industrial food processing (roasting, drying, and so on), high-temperature cooking (frying, grilling, and so on), or environmental exposure (incomplete combustion of fossil fuels or wood, and so on). In edible oils, the seed and kernel drying process is thought to be the most prominent source of PAHs with the use of direct firing. High temperatures used in the seed roasting process is another possibility for contamination in edible oils. Environmental exposures, such as plants exposed to industrial and vehicle emissions, could also contribute to PAHs found in edible oils. Due to the lipophilic nature of PAHs, fats and lipids present the main source of PAHs in the diet. Since, the European Commission (EC) Regulation established maximum levels of benzo(a)pyrene in different food groups along with other PAH analytes as carcinogenic by the Scientific Committee on Food (SCF). The Joint FAO/WHO Expert Committee on Food Additives (JECFA) identified benzo(c)fluorene as a PAH that should be monitored as well. EC Regulations 88/ and 8/ set the maximum permitted levels of PAH residues in oils and fats intended for human consumption or use as an ingredient in food to. µg/kg for benzo(a)pyrene and µg/kg for the sum of benzo(a)pyrene, benzo(a) anthracene, benzo(b)fluoranthene, and chrysene,4. Agilent Enhanced Matrix Removal Lipid (EMR Lipid) dspe cleanup has gained a lot of attention since its introduction in. The EMR Lipid dspe sorbent selectively interacts with the unbranched hydrocarbon chains of lipids, and leaves the bulky target analytes in solution for subsequent analysis. This makes EMR Lipid ideal for multiclass and multiresidue analysis. The EMR Lipid sorbent is convenient and effective in removing matrix interference, particularly lipids, to allow for low-level detection of the analyte of interest,. After EMR Lipid dspe cleanup, residual water is removed using an EMR Polish dispersive kit containing MgSO 4 and NaCl, which is crucial for GC/MS/MS analysis. Then, a PSA/C8/MgSO 4 dspe cleanup was used for further matrix cleanup and water removal. The challenge of analyzing PAHs is due to their chemical properties, therefore, GC/MS/MS was modified for analysis. PAHs tend to adhere to surfaces, are subject to desublimation, and are difficult to vaporize. Thus, the GC inlet, MSD transfer line, and MSD source were kept at high temperatures to minimize surface contact and improve vaporization. JetClean keeps the source clean by introducing a low flow of hydrogen during data acquisition 8. The inlet liner contains glass wool to transfer heat and prevent PAHs from depositing at the bottom of the liner. Backflushing maintains column lifetime by removing heavy eluting matrix at the end of each analysis 9. Since PAHs are resistant to change, a high collision energy of ev was used in all of PAH MRM acquisitions to remove matrix interference while PAHs remained unaffected. This Application Note investigated pumpkin seed oil because the matrix is fatty and complex with a high probability for PAH contamination. The fatty acid compositions in pumpkin seed oil include mainly palmitic acid (9. to 4. %), stearic acid (. to.4 %), oleic acid ( to 4.9 %), and linoleic acid ( to.8 %). Pumpkin seed oil is produced by toasting pumpkin seeds above C, and pressing the seeds, using a hydraulic press, into a dark green oil. In addition to the roasting process, the other possibility for PAH contamination in pumpkin seed oil is that there is no refining step, which can drastically decrease the amount of PAHs. Experimental Solvents and sample preparation products Solvents used in this study were HPLCor GC-grade. Acetonitrile (ACN) (4) and isooctane (49) were bought from Sigma-Aldrich. Sample preparation products used for sample cleanup consisted of the following: Bond Elut EMR Lipid dispersive SPE in ml tube (EMR Lipid) (p/n ) Bond Elut EMR Lipid Polish in ml tube containing NaCl and anhydrous MgSO 4 (EMR Polish) (p/n -) QuEChERS dispersive SPE, EN method, in ml tube containing mg PSA, mg C8EC, and 9 mg of MgSO 4 (PSA/C8/MgSO 4 ) (p/n -)

Standards and solutions The PAH standard mix (STD) consisted of PAH standard mix (p/n 9-48). Isotopically labeled internal standard mix (IS) consisted of deuterated PAHs (p/n 9-49). For prespiking quality control (QC) samples, neat STD and IS spiking solutions were prepared in isooctane at desired concentrations, and spiked directly into pumpkin seed oil. For postspiking matrix-matched calibration samples, neat STD and IS spiking solution were prepared in isooctane at desired concentrations, and used to reconstitute dried matrix blank (MB) samples. Prespiking and postspiking levels were,, and ng/g STD with ng/g IS. Matrix-matched calibration levels were,,,,,, and ng/g STD with ng/g IS. Sample preparation Store-bought toasted pumpkin seed oil was used in this study. The sample was extracted with ACN followed by sample cleanup using EMR Lipid, with residual water removed using EMR Polish. The PSA/C8/MgSO 4 cleanup was used for further matrix cleanup and water removal. Figure shows the detailed procedure for sample preparation. GC/MS/MS analysis The GC/MS/MS used in this study is an Agilent 89B GC and an Agilent triple quadrupole GC/MS equipped with JetClean self-cleaning ion source and an Agilent 9A Automatic Liquid Sampler (ALS). Tables to and Figure list detailed GC and MSD parameters. Data were acquired using MassHunter GC/MS Acquisition B.., and analyzed using MassHunter Qualitative Analysis B.. and MassHunter Quantitative Analysis B.9.. Figure. Detailed procedure to prepare pumpkin seed oil sample for GC/MS/MS analysis. CFT. Extraction Weigh g of pumpkin seed oil into a ml centrifuge tube. QC samples: prespike PAH STD and IS spiking solution into the oil. Create MB samples that do not contain STD and IS for matrix-matched calibration Vortex for two minutes at, rpm. Add ml of ACN, vortex for minutes at, rpm, and centrifuge for minutes at, rpm.. EMR Lipid cleanup Add. ml of water to EMR Lipid, and vortex to mix. Transfer ml of supernatant (from the extraction step) to the EMR Lipid tube. Vortex for two minutes at, rpm and centrifuge for five minutes at, rpm.. EMR Polish Decant supernatant to EMR Polish. Vortex and shake vigorously. Centrifuge for five minutes at, rpm. 4. PSA/C8/MgSO 4 cleanup Transfer supernatant to PSA/C8/MgSO 4. Vortex for two minutes at, rpm and centrifuge for five minutes at, rpm.. Concentration Transfer ml of supernatant to a glass centrifuge tube. Concentrate the sample to dryness (N flow at 4 C water bath). Reconstitute dried samples (x) Matrix-matched calibration: postspike MB with µl postspiking solution. QC samples: Add µl of isooctane. Vortex for two minutes at, rpm, sonicate for seconds in a water bath, and centrifuge for seconds. Transfer to an autosampler vial with a µl glass insert for GC/MS/MS analysis. ALS Plug m Select PAH column m Select PAH column Helium carrier gas GC oven JetClean Hydrogen EI MS/MS HES Source: C Quads: C Transfer line: C Figure. GC/MS/MS in electron ionization (EI) mode configured with BF and JetClean. Arrows indicate direction of helium carrier gas flow. CFT purged -way splitter is used to configure the two columns for BF. The JetClean self-cleaning ion source is configured to the MSD in Acquire and Clean mode to allow. ml/min of hydrogen flow to the source. ALS = automatic liquid sampler. HES = high efficiency source. CFT = Capillary Flow Technology.

The following GC/MS/MS modifications are crucial for low level PAH analysis: BF setup (Figure ) Cut m off the Select PAH column ( m length µm diameter. µm film thickness). Connect the m section from the split/splitless inlet to the capillary flow technology (CFT). Connect the rest of the m from the CFT to the mass spectrometer detector (MSD). Use the BF Wizard in the acquisition software for the following postrun procedures: Decrease inlet pressure to psi. Increase CFT pressure to psi. Maintain an oven temperature of C. Use void volumes, giving a run time of.8 minutes. Inlet, transfer line, and source temperatures are at,, and C, respectively. The inlet liner must be an Ultra Inert 4 mm, single tapered with glass wool (to transfer heat to the PAHs). Operate the JetClean self-cleaning ion source in Acquire and Clean mode at. ml/min of hydrogen flow to the source. RT Lock to chrysene at.89 minutes to prevent shifting in retention time, and enable easy maintenance. Table. GC parameters. GC Inlet Mode 89B GC system Split/splitless Splitless Heater C Pressure Total Flow Septum Purge Flow Septum Purge Flow Mode Purge Flow to Split Vent 4.4 psi 4. ml/min ml/min Switched ml/min at minute GC Conditions Inlet Liner Agilent 4 mm Ultra Inert inlet liner, single tapered with glass wool, 9 µl (p/n 9-9) Oven Ramp Total Run Time* Column Dimension Dimensions In Out Pressure Flow Mode Oven Initial: 8 C (Hold. minutes) Ramp : Rate at C/min to C Ramp : Rate at 4 C/min to 8 C Ramp : Rate at C/min to 8 C Ramp 4: Rate at C/min to C (Hold 4 minutes).8 minutes Column Setup For Backflush Agilent Select PAH (p/n CP4) m length µm diameter,. µm film thickness Column m µm,. µm ( m cut from m column) Split/splitless inlet BF EPC 4.4 psi. ml/min Constant flow Column Dimensions m µm,. µm (Remaining after m removed to make column ) Main Segment 4.8 m heated by oven Segment. m heated by Thermal Aux In Out Pressure Flow Mode Carrier Gas RT Locking BF EPC MSD. psi. ml/min Constant flow Helium Locked to chrysene at.89 minutes* * Instrument dependent 4

BF Operating Conditions Oven Temperature C BF Pressure Inlet Pressure During BF psi psi Void Volumes BF Time BF Flow to Inlet Injector.8 minutes 9.4 ml/min 9A Automatic Liquid Sampler Injection Volume µl Syringe Size µl Syringe G4-8 Viscosity Delay seconds Thermal Aux (MSD Transfer Line) Heater C Table. MS parameters. Table. MRM transitions and scan segment. MSD Conditions MSD Ion source triple quadrupole LC/MS Electron ionization Analyte a RT (min) b Quantifier c Qualifier c (ms) Dwell Cycles per s ms per Cycle Scan type MRM Electron energy ev Solvent delay 4 minutes MS source C MS quads C Gain Collision Cell He quench gas 4 ml/min N collision gas. ml/min JetClean benzo(c)fluorene.. &.. &..4 benzo(a)anthracene-d. 4. & 4. 4. & 8..4.8 benzo(a)anthracene. 8. & 8. 8. &..4.8 chrysene-d.8 4. & 4. 4. & 8..4.8 cyclopenta(cd)pyrene.9. &.. &..4.8 chrysene 8. 8. & 8. 8. &..4.8 -methylchrysene. 4. & 4. 4. & 4..4 9. benzo(b)fluoranthene-d. 4. & 4. 4. &... benzo(b)fluoranthene.8. &.. &... Operation Hydrogen flow Acquire and Clean. ml/min benzo(k)fluoranthene-d.8 4. & 4. 4. &... benzo(k)fluoranthene.9. &.. &... benzo(j)fluoranthene.. &.. &... benzo(e)pyrene.. &.. &.. 8. benzo(a)pyrene-d. 4. & 4. 4. &.. 8. benzo(a)pyrene.. &.. &.. 8. dibenzo(ah)anthracene-d 4 4. 9. & 9. 9. & 9..4. indeno(,,-cd)pyrene-d 4.8 88. & 88. 88. & 8..4. dibenzo(ah)anthracene 4.8 8. &. 8. & 8..4. indeno(,,-cd)pyrene 4.8. & 4.. &..4. benzo(ghi)perylene-d 4. 88. & 88. 88. & 8.. 9.4 benzo(ghi)perylene 4.. &.. & 4.. 9.4 a Isotopically labeled compounds (-d and -d 4 ) are used as internal standards (p/n 9-49). All other analytes are from a PAH standard mix (p/n 9-48). Gain =. b Retention times are system-dependent c Collision energy is ev for quantifier and qualifier MRM transitions for all analytes and internal standards. Quantifier ions were chosen based on abundance and least interference. Unit resolution (. amu) was used for all precursor and product ions.

Results and discussion EMR Lipid sample preparation EMR Lipid dspe cleanup was modified specifically for PAH analysis in oil matrices. Pumpkin seed oil is a fatty and hydrophobic matrix that binds strongly to the highly hydrophobic PAH analytes. EMR Lipid dspe cleanup usually requires the use of % water in the sample mixture to achieve efficient lipid removal. However, the addition of % water reduces PAH solubility and negatively impacts analyte recoveries; therefore, the amount of water for EMR Lipid sorbent activation was reduced to. ml (conventionally ml). Pumpkin seed oil extract was then added immediately to the EMR Lipid sorbent to ensure maximum interaction with the sorbent. EMR Polish dspe is normally recommended for residual water removal, but for GC/MS/MS analysis, this one-step water removal is not adequate, and an additional drying step is necessary. Therefore, the PSA/C8/MgSO 4 dspe cleanup was used for further matrix and complete water removal. To achieve the desired quantitation limit of PAHs for GC/MS/MS analysis, the sample was concentrated and reconstituted times with isooctane. MS full scans were used to evaluate the matrix cleanup efficiency using EMR Lipid dspe cleanup. Without sample cleanup, pumpkin seed oil showed matrix and lipid interferences with raised baselines and column overload (Figure ). Three methods of sample cleanup were compared: PSA/C8/MgSO 4 dspe EMR Lipid dspe EMR Lipid dspe and PSA/C8/MgSO 4 dspe EMR Lipid with additional PSA/C8/MgSO 4 cleanup was the most efficient cleanup for lipid and other matrix interference. Counts No cleanup 4. PSA/C8/MgSO 4 4.4 EMR Lipid 4. EMR Lipid + PSA/C8/MgSO 4 4..8..4...8..4...8..4...8..4. 8 4 8 4 8 4 8 4 4 44 4 48 Figure. Pumpkin seed oil extracts with different cleanup procedures. MS scan range m/z 4 to,. Black: no cleanup. Blue: PSA/C8/MgSO 4 cleanup. Green: EMR Lipid cleanup. Red: EMR Lipid with an additional PSA/C8/MgSO 4 cleanup.

GC/MS/MS analysis Low-level PAH quantification was feasible in pumpkin seed oil by GC/MS/MS modified with JetClean and BF. The JetClean self-cleaning ion source is a module that introduces a low flow of hydrogen directly into the source during data acquisition to eliminate matrix deposition. BF reduces sample carryover by reversing the flow of the first column to flush out high-boiling matrix contaminants through the split vent at the end of analysis. The advantage of BF is that contaminants are not deposited onto the source. Without the need for column bake-out, the lifetime of the column is maintained, which also prevents column bleed from depositing onto the source. MRM and a high collision energy (CE) were used for PAH analysis in pumpkin seed oil. Quantifier and qualifier ions were chosen based on ion abundance and significance. Since PAHs do not fragment readily, the precursor and product ion for the quantifier transitions is the molecular mass to the molecular mass ([M] + & [M] + ). The qualifier transition is analyzed at [M] + & [M-] +. The high CE of ev helped eliminate matrix interference, while PAH remained unaffected (Figure 4). Table 4 lists the MRM transitions. Counts... 4.8 4.4 4....8 4-8 9. Benzo(c)fluorene. Benzo(a)anthracene. Cyclopenta(cd)pyrene 4. Chrysene. -Methylchrysene. Benzo(b)fluoranthene. Benzo(k)fluoranthene 8. Benzo(j)fluoranthene 9. Benzo(e)pyrene. Benzo(a)pyrene. Dibenzo(ah)anthracene. Indeno(-cd)pyrene. Benzo(ghi)perylene.4..,...4 4 8 9 4 8 9 4 4 4 4 Figure 4. MRM TIC of quantifier ion from matrix-matched calibration of pumpkin seed oil spiked with ng/g PAH. Collision energy of ev. Quantifier transitions [M] + & [M] + are plotted, where M represents molecular mass.

Counts...9.8....4... -. -. A Benzo(a)anthracene MW: 8 Cyclopenta(cd)pyrene MW: Chrysene MW: 8 B Dibenzo(ah)anthracene MW: 8 Indeno(-cd)pyrene MW:...4....8.9 8. 8. 8. 8. 4.4 4.8 4. 4. 4.8 4.84 4.88 4.9 4.9 4. 4.4 4.8 4.. C Benzo(k)fluoranthene. MW: Benzo(e)pyrene MW:.9...9.8....4... -..8. Benzo(b)fluoranthene MW: Benzo(j)fluoranthene MW: Counts...4 Benzo(a)pyrene MW:... -.....8.9.....4....8.9.....4.. Figure. GC/MS/MS MRM chromatograms of pumpkin seed oil spiked with ng/g PAHs (A-E). Collision energy of ev. Quantifier transitions [M] + & [M] + are plotted, where M represents molecular mass. 8

The Select PAH column provided excellent separation, good peak shape, and sensitivity for the pairs of PAH compounds that are typically difficult to separate on most GC columns because of their identical mass fragmentations. The column aided in separation of the following PAH compound pairs that were investigated in this study (Figures A-C). benz(a)anthracene, cyclopenta(c,d)pyrene, and chrysene (molecular mass, 8 Da) Indeno(,,-cd)pyrene and dibenzo(a,h)anthracene (molecular mass, 8 Da) benzo(b)fluoranthene, benzo(k)fluoranthene, and benzo(j)fluoranthene (molecular mass Da) benzo(e)pyrene and benzo(a)pyrene (molecular mass Da) Sensitivity, peak shape, and separation were also observed at the prespike level of ng/g of the four PAHs monitored by the EU Commission Regulation (Figure ). A Benzo(a) anthracene MW: 8 Chrysene MW: 8 B Benzo(k)fluoranthene MW: Benzo(j)fluoranthene MW: C Benzo(e)pyrene MW: Benzo(a)pyrene MW: Benzo(b)fluoranthene MW: Counts Figure. MRM TIC of pumpkin seed oil was prespiked with ng/g PAH. 9

Accuracy and precision Excellent accuracy and precision were achieved at,, and ng/g in pumpkin seed oil using the developed sample preparation method. The accuracy ranged between 9 and 8 % for all spiking levels of analytes analyzed using IS correction (Figure A). All compounds at all spiked levels fell in the range of 8 to % accuracy, except for benzo(k)fluoranthene, which was 9 % at the ng/g prespike level. The RSD ranged between and % (Figure B). Cyclopenta(cd)pyrene and -methylchrysene at ng/g were not detected. LOQs and calibration linearity A seven-point matrix-matched calibration was used for method quantitation. Matrix-matched calibration curves were generated at,,,,,, and ng/g of PAHs with ng/g of ISTD. Linear calibration was observed with an R >.99 using linear regression with weight of /x (Table ). LOQs were ng/g except for cyclopenta(cd)pyrene and -methylchrysene at ng/g. A 9 Table. Pumpkin seed oil seven-point matrix-matched calibration. Analyte LOQ R Accuracy (%) 4 8 4 Benzo(c)fluorene RSD (%) 9 9 9 Benzo(a)anthracene B Benzo(c)fluorene 8 8 8 Cyclopenta(cd)pyrene Benzo(a)anthracene Cyclopenta(cd)pyrene 4 8 8 Chrysene 89 9 -Methylchrysene Chrysene 4 9 Benzo(b)fluoranthene -Methylchrysene 8 Benzo(b)fluoranthene 9 99 Benzo(k)fluoranthene Benzo(k)fluoranthene 4 4 Benzo(j)fluoranthene 4 Benzo(j)fluoranthene 9 Benzo(e)pyrene Benzo(e)pyrene 4 9 Benzo(a)pyrene 99 9 Dibenzo(ah)anthracene Benzo(a)pyrene ng/g 8 to % ng/g ng/g 4 Dibenzo(ah)anthracene 99 9 Indeno(-cd)pyrene Indeno(-cd)pyrene 9 Benzo(ghi)perylene ng/g % ng/g ng/g Benzo(ghi)perylene Figure. Accuracy (A) and Precision (B) of pumpkin seed oil spiked with,, and ng/g PAH standard mix. IS was spiked at ng/g. Analytes are plotted in order of increasing retention time. n =. Bbenzo(c)fluorene.999 Benzo(a)anthracene.99 Cyclopenta(cd)pyrene.9949 Chrysene.99 -Methylchrysene.9 Benzo(b)fluoranthene.9 Benzo(k)fluoranthene.9 Benzo(j)fluoranthene.99 Benzo(e)pyrene.99 Benzo(a)pyrene.99 Dibenzo(ah)anthracene.9994 Indeno(-cd)pyrene.9 Benzo(ghi)perylene.98

Recovery Absolute recovery ranged from to 94 % without the use of IS (Figure A). RSD of recovery ranged from to % (Figure B). The PAH absolute recoveries decrease with increasing molecular weight due to the decreasing PAH solubility in acetonitrile during the extraction step. Overall, the recoveries were within the limits set by the EU Commission Regulation of to % except for benzo(e)pyrene, benzo(a)pyrene, dibenzo(ah)anthracene, indeno(-cd)pyrene, and benzo(ghi)perylene at some spiked levels. Benzo(e)pyrene and benzo(a)pyrene recoveries were 4 and 44 % at ng/g spiked level, respectively. Dibenzo(ah)anthracene recoveries were and 9 % at the and ng/g spiked levels, respectively. Indeno(-cd)pyrene recoveries were 8 and % at the and ng/g spiked levels, respectively. Benzo(ghi)perylene recoveries ranged from 4,, and 4 % at,, and ng/g spiked levels. RSD% values were below % for all analytes except benzo(a)pyrene with %. However, the low recoveries can be corrected using IS for quantitation. Cyclopenta(cd)pyrene and -methylchrysene at ng/g were not detected. Conclusions A method was developed and validated for PAH analysis in pumpkin seed oil using liquid-liquid extraction followed by Bond Elut EMR Lipid dspe and PSA/C8/MgSO 4 cleanup by GC/MS/MS. EMR Lipid dspe cleanup was modified Accuracy (%) 4 8 4 A 9 Benzo(c)fluorene RSD (%) 4 Benzo(a)anthracene B Benzo(c)fluorene 84 Cyclopenta(cd)pyrene 8 Benzo(a)anthracene 94 Cyclopenta(cd)pyrene 9 Chrysene -Methylchrysene Chrysene 9 Figure 8. Recovery (A) and RSD (B) of pumpkin seed oil spiked with ng/g (blue), ng/g (yellow), and ng/g (green) PAH standards. n=. Analytes are plotted in order of increasing retention time. using less water for sorbent activation to improve the PAH recoveries during cleanup. GC/MS/MS was modified with JetClean and BF. These modifications allowed for recoveries that are within the limits of to % for most of the EU priority PAHs. Calibration linearity was achieved with R >.99. Benzo(b)fluoranthene -Methylchrysene Benzo(b)fluoranthene Benzo(k)fluoranthene 8 Benzo(k)fluoranthene Benzo(j)fluoranthene 8 Benzo(j)fluoranthene 4 Benzo(e)pyrene Benzo(e)pyrene 44 Benzo(a)pyrene 8 9 Dibenzo(ah)anthracene 9 Benzo(a)pyrene ng/g to % ng/g ng/g 8 Accuracy was within ± % except for benzo(k)fluoranthene, which was 9 % at the prespiked level of ng/g. Precision was below % for all analytes. Recoveries were within the EU Commission Regulation limit of to % for most of the mideluters, but present challenges for the heavier PAHs. This could be a result of PAH solubility to acetonitrile during extraction. 8 Dibenzo(ah)anthracene Indeno(-cd)pyrene Indeno(-cd)pyrene Benzo(ghi)perylene ng/g % ng/g ng/g 9 8 4 4 9 Benzo(ghi)perylene 4

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