Quantitative Analysis and Identification of Migrants in Food Packaging Using LC-MS/MS

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Quantitative Analysis and Identification of Migrants in Food Packaging Using LC-MS/MS Cécile Busset 1 and Stephen J. Lock 2 1 AB SCIEX, Paris (France); 2 AB SCIEX, Warrington, Cheshire (U.K.) Introduction Packaging improves the quality and safety assurance of food, especially from micro-organisms, biological and chemical contaminants. Packaging is therefore an essential component for the food industry and the manufacturing processes. However, over the last couple of years there has been a growth in the number of materials and substances used in food packaging so in order to improve food safety a migration study for compounds is becoming more important to prevent the use of compounds that can migrate into food. Currently, an upper limit for the overall migration of 6 mg/kg or 1 mg/dm 2 has been set by the European Union (EU). 1 In the USA, the regulations for food packaging material are more complex, because the types of raw and processed foods, and conditions of use are separated. 2 In this study three compounds:,, and are investigated (Figure 1). is a mixture of 2- Isopropylthioxanthone and 4-Isopropylthioxanthone. contains 819 (Phenylbis (2,4,6-trimethylbenzoyl) phosphine oxide. Both are used as photo-initiators in UV cured inks. (Tri(propylene glycol) diacrylate is an ingredient of cured inks. The data presented discusses linearity of response, robustness and the use of the Multiple Reaction Monitoring combined with Enhanced Product Ion scanning (MRM-EPI) using an AB SCIEX 32 QTRAP LC/MS/MS System as a way of gaining additional information for the presence of these migrants. Experimental Sample Extraction Standards were prepared in the solvent composition at the start of the LC run (water/acetonitrile +.1% formic acid 7/3). Three sorts of real samples were analyzed: a packaging cap with only decoration (inks), a packaging cap with only varnish and a packaging cap with decoration and varnish. 1 dm 2 of each sample was extracted with acetonitrile. The extracted sample was evaporated and reconstituted in initial mobile phase before analysis. LC An Agilent 12 system containing a binary pump flowing at 25 µl/min, autosampler, and a column oven set at 2 C were used with a Hypersil BDS C18 column (5 µm, 1 x 2 mm). 1 µl injections of standards and extracts were separated using a gradient (Table 1) of mobile phase A (.1 % formic acid in water) and B (.1 % formic acid in acetonitrile). 5 minutes column equilibration time was used between runs. p 1

2-4- Table 2. MS/MS conditions Compound Q1 Mass (amu) Q3 Mass (amu) DP (V) CE (V) 255.1 66 35 S S 255.1 184.1 66 61 419.2 147.2 21 23 CH 2 419.2 119.2 21 57 31.2 113.2 21 13 H 2 C P Figure 1. Investigated migrants from food packaging Table 1. LC gradient Experiment 1 triggered three EPI scans at collision energies (CE) of 2; 35 and 5 V. Experiment 2 used a single dependent scan with a CE of 35 V and Collision Energy Spread (CES) of 15 V. CES was found to give more reproducible and richer MS/MS spectra, in comparison to dedicated and fixed Collision Energies, and thus greatly enhancing the quality of library searching. The scan speed of the EPI scans were 4 amu/s and Dynamic Fill Time (DFT) was used for all EPI scans. In both experiments peaks were identified in the MRM survey using Dynamic Background Subtraction (DBS). Step Time (min) % A % B 5. 7 3 1 2. 5 95 2 7. 5 95 3 7.1 7 3 4 12. 7 3 MS/MS All experiments were performed on an AB SCIEX 32 QTRAP LC/MS/MS System with Turbo V source at 45 C using Electrospray Ionization (ESI) in positive polarity. The following source conditions were used: Curtain Gas (CUR) IonSpray Voltage (IS) Gas1 Gas2 25 psi 5 V 4 psi 5 psi CAD Gas Medium Temperature 45 C Analyses were based on two different Information Dependent Acquisition (IDA) experiments using Multiple Reaction Monitoring (MRM) in the survey scan and dependent Enhanced Product Ion (EPI) scanning. MRM transitions were previously optimized (see Table 2). A dwell time of 1 ms was used for each transition and the pause time was set to 5 ms. Identification of analytes in the real samples was based on searching against the mass spectral library created from MRM- EPI analyses of standards. Results and Discussion Standards at 1 ng/ml were used to build a mass spectral library. An example of reference spectra is shown in Figure 2. Standards were used over a range.1 to 1 ng/ml to produce calibration lines. +EPI (255.13) Charge (+) CE (2) FT (25): Exp 2, 72 t... 255.2 Max. 2.6e5 cps. +EPI (255.13) Charge (+) CE (35) FT (25): Exp 2, 31 t... Max. 1.2e5 cps. 1.e5 184.1 255.2 +EPI (255.13) Charge (+) CE (5) FT (25): Exp 2, 62 t... Max. 4.6e4 cps. 184.1 152.2 CE = 2V CE = 35V CE = 5V +EPI (255.13) Charge (+) CE (35) CES (15) FT (25): Exp... Max. 1.8e5 cps. 255.2 CE = 35V with CES = 15V 184.2 152.2 215.6 239.2 Figure 2. An example of the effect of collision energy on the EPI spectra of a migrant standard used for generating library data (1 ng/ml standard) p 2

Figure 3 shows calibration lines that were obtained from standards analyzed in MRM-EPI mode with each standard analyzed in duplicate. The r values obtained from these calibration lines (.5 5 ng/ml for, 2 1 ng/ml for and.5 1 ng/ml for ) were greater than.996 when a linear fit with 1/x weighting was applied. XIC of +MRM (6 pairs): 31.2/113.2 Da from Sample 7 (std2... 5.4e4 4.5e4 3.5e4 4.3 Max. 5.4e4 cps. quant.rdb ( 1): "Linear" Regression ("1 / x" weighting): y = 5.88e+3 x + 3.14e+3 (r =.996) 3.e6 2.e6 1.e6 Concentration, ng/ml quant.rdb (Irga 1): "Linear" Regression ("1 / x" weighting): y = 226 x + 19 (r =.9994) 2.4e5 1 2 3 4 5 6 7 8 9 1 Concentration, ppb quant.rdb ( 1): "Linear" Regression ("1 / x" weighting): y = 3.27e+3 x + 274 (r =.9993) 3.e6 2.e6 1.e6 r =.996 r =.9994 r =.9993 1 2 3 4 5 6 7 8 9 1 Concentration, ng/ml Figure 3. Calibration lines obtained from, and with r values >.996 (no internal standard used) 3.e4 2.5e4 1.5e4 1.e4 5 Figure 4. 1 µl injection of migrants standards in initial mobile phase Table 4. Estimates for limits of detection (LD), limits of quantitation LQ), and linearity for food migrants Compound S/N (at ng/ml) LD (ng/ml) LQ (ng/ml) Linearity (ng/ml) 4.4 (.5) 4.12.12-5 18.4 (2.).33.5.5-1 Repeatability and %CV were assayed by 5 repeat injections of a standard close to the limits of quantitation of each analyte and results are summarized in Table 3 with all coefficients of variation <1% (no internal standard was used). Table 3. Reproducibility data from 5 replicate injections Compound Transition Concentration (ng/ml) % CV (n=5) 255.1/.5 8.2 419.2/147.2.844 5.2 23.2 (.5).2.6.6-1 8 6 4 2 Max. 92 cps. 5.7 145 1 5 Max. 145. cps. Figure 5. Signal to noise (S/N) of low level migrant standards (S/N calculated using peak-to-peak algorithm) 5.6 338 3 Max. 337.5 cps. S/N = 4.4 S/N = 18.4 S/N = 23.2.5 ng/ml 2 ng/ml 25 2 15 1 5 4.1.5 ng/ml 31.2/113.2.515 9.5 Figure 4 shows a typical trace obtained from the analysis of migrant standard prepared in the initial mobile phase, all migrants were detected below 1 ng/ml as shown in Table 4 with Figure 5 giving the sensitivity of migrants at a concentration of.5 ng/ml ( and ) and 2 ng/ml (). This MRM data was then used to quantify migrants in cap extracts, examples of various extracts are given in Figures 6 and concentrations of migrants were summarized in Table 5. p 3

Max. 2.6e5 cps. Max. 1.4e5 cps. 2.5e5 Deco* Max. 1.6e5 cps. 1.4e5 1.2e5 8.e4 Deco Max. 7.1e4 cps. Varnish* 7.1e4 Varnish 8. Max. 3.1e5 cps. 5.2 8. Max. 1.3e5 cps. 3.e5 2.5e5 Deco + varnish* 1.2e5 Deco + varnish 8.e4 Figure 6. A comparison of food packaging samples extracted with acetonitrile and where the acetonitrile extract of the same sample had been evaporated to dryness and reconstituted in mobile phase* (cap with decoration (top), cap sealed with varnish (middle), and cap with decoration and sealed with varnish (bottom)) p 4

Table 5. Quantitation results from real samples (* sample was evaporated to dryness and reconstituted in the same volume of mobile phase A to improve HPLC peak shape) Extract (ng/dm²) (ng/dm²) (ng/dm²) Deco 4.43 632 5.39 Deco* 4.96 4347 5.77 Varnish 8 394.67 Varnish*.54 21.69 Deco + varnish 4.65 675 3.97 Deco + varnish* 4.26 3687 3.99 To further identify the migrant the automatically acquired EPI spectra was searched against a mass spectral library previously created with spectra obtained from 1 ng/ml standards. DBS enabled the acquisition of high quality MS/MS spectra even for co-eluting compounds. The Purity Fit shown in Table 6 indicated if the spectrum, in the extract, was a good match for the library spectrum, generally a fit above 7% indicated a positive identification of the migrant in the extract. Table 6. The Purity Fit (%) results taken from the spectra obtained from contaminants in real samples when compared with those in a library of spectra of standards (* sample was evaporated to dryness and reconstituted in the same volume of mobile phase A to improve HPLC peak shape) Summary The LC-MS/MS method developed can be used for quantitation of migrants in food packaging material. The sensitivity levels of the 32 QTRAP system were high enough to detect migrants at 1 mg/kg in extracts. A mass spectral library containing of EPI spectra at different standardized Collision Energy and Collision Energy Spread values can then be used to identify the compound at the required matrix detection levels, enabling direct injection analysis on extracts. Acknowledgements We acknowledge Mr Philippe Tourelle and Gilles Jarry of the society Impress Metal Packaging (France) for supplying extracts and samples. References 1 2 European Commission Health & Consumer Protection Directorate general - SANC D3/AS D(25) FDA 21 CFR 17.1 - Submission of a premarket notification for a food contact substance (FCN) to the Food and Drug Administration (FDA). Code of Federal Regulations (December 25) Extract (%) (%) (%) Deco 78 88 81 Deco* 87 28 31 Varnish 63 6 98 Varnish* 34 81 44 Deco + varnish 97 45 Deco + varnish* 91 57 95 For Research Use nly. Not for use in diagnostic procedures. 21 AB SCIEX. The trademarks mentioned herein are the property of AB Sciex Pte. Ltd. or their respective owners. AB SCIEX is being used under license. Publication number: 18321-1 Headquarters International Sales 353 Hatch Drive Foster City CA 353 Hatch Drive Foster City CA 9444 USA For our office locations please call the division Phone 65-638-58 headquarters or refer to our website at www.absciex.com www.absciex.com/offices