International Journal of Analytical Chemistry

International Journal of Analytical Chemistry / 2021 / Article

Research Article | Open Access

Volume 2021 |Article ID 6654611 | https://doi.org/10.1155/2021/6654611

Vicent Yusà, Antonio López, Pablo Dualde, Olga Pardo, Igor Fochi, Pablo Miralles, Clara Coscollá, "Identification of 24 Unknown Substances (NIAS/IAS) from Food Contact Polycarbonate by LC-Orbitrap Tribrid HRMS-DDMS3: Safety Assessment", International Journal of Analytical Chemistry, vol. 2021, Article ID 6654611, 13 pages, 2021. https://doi.org/10.1155/2021/6654611

Identification of 24 Unknown Substances (NIAS/IAS) from Food Contact Polycarbonate by LC-Orbitrap Tribrid HRMS-DDMS3: Safety Assessment

Academic Editor: Chanbasha Basheer
Received18 Nov 2020
Revised17 Feb 2021
Accepted25 Feb 2021
Published27 Mar 2021

Abstract

Twenty-four substances, mainly NIAS, have been tentatively identified in food contact polycarbonate through the application a new, fast, and automated analytical strategy for the investigation of unknowns in food contact materials. Most of the identified compounds were plasticizers, slip agents, antioxidants, and ultraviolet stabilizers and fragrances, and the majority of them have not been previously identified in PC food contact materials. The workflow setup includes an intelligent data acquisition applied using LC-Orbitrap Tribrid-HRMS (MS3), with an automated data processing using Compound DiscovererTM. To obtain a high confidence identification of unknown substances, a very strict criterion has been established, which comprises exact mass, isotopic profile, MS2 match, retention time, and MS3 match. To check for the safety of the migration from the food contact polycarbonate, a risk assessment was achieved using the threshold of the toxicological concern (TTC) approach. Except for the slip agent hexadecanamide, the compounds tentatively identified do not represent a risk.

1. Introduction

Plastics for food contact applications must be safe. In Europe, plastic articles may only be placed on the market as food contact materials (FCM) if they are manufactured with substances (monomers, additives, and aids) included in the list incorporated into the Regulation 10/2011 [1] (intentionally added substances, IAS). However, during their manufacturing and use, some impurities and reaction or degradation products can be formed (nonintentionally added substances, NIAS). The potential risk of NIAS should be considered for authorization [2, 3] and for the declaration of compliance at the marketing stages [4].

Between the different thermoplastic materials used as FCM, polycarbonate (PC) is commonly employed for tableware and containers exposed to hot filling or heating after filling, such as plates and bowls, that could be used repeatedly. These PC containers can also be used for reheating food in a microwave oven [5]. Many ambient factors such as temperature, humidity, light together with the repeated uses, and washing cycles can damage the stability of the material and increase the migration of substances to the food [6]. The main concern about degradation of PC food containers is the release of bisphenol A (BPA), a component monomer of PC that is currently of toxicological concern [7, 8].

To assess the safety of food contact plastic materials, appropriate analytical methods are required [9]. Apart from the target analysis, mainly for detection of IAS or specific contaminants, the analysis of NIAS is mandatory to avoid any potential health risk to the consumer [2] and should be performed in accordance with the Regulations 1935/2004 [4] and 10/2011 [1]. The identification of NIAS is challenging and requires a non-target analytical approach [10, 11] using LC-HRMS (Q-Orbitrap/Q-TOF), performed using two main modes, data-dependent acquisition (DDA) and data-independent acquisition (DIA) [12].

Bignardi et al. [13] employed a target and untargeted method, using LC-HRMS-Orbitrap working in the data-dependent acquisition mode (DDA), for characterization of PC food contact plastic. In the target approach, several plastic additives were identified. With the untargeted analysis, some colorants and several oligomers derived from the chain breakage were identified, following a laborious and time-consuming process. In a recent study, the same research team [14] applied the target method with UHPLC-HRMS to determine the migration from PC tableware objects, detecting oligomers from the PC chain and traces of colouring agents.

To perform an exhaustive characterization of NIAs, an extensive acquisition (DDA including Full Scan and MSn) and identification of the unknown substances is necessary. This is challenging because of the large number of features present both in the samples and the background (blanks and/or matrix). In order to automate these procedures, new acquisition tools are developed for background removing, exhaustive precursor selection (inclusion list), and creation of dynamic and real-time exclusion list [15]. Likewise, an automated library search has been improved through the data processing tool Compound Discoverer™ [16].

For the identified NIAS, a risk assessment is necessary to ensure the safe usage of the PC containers. One practical option is to use the threshold of the toxicological concern (TTC) approach that estimates the theoretical toxicity of compounds linked to their molecular structure, and a threshold value is provided below which there is a very low probability of adverse health effects [17, 18].

In this study, a new approach for the determination of unknown substances in PC bowls used for food container was investigated. We evaluated the capacity for exhaustive spectral data acquisition of an innovative intelligent acquisition mode (AcquireX™) using DD-MS3. In the second phase, the automatic search on compound libraries and spectral databases was employed to putative identification of unknown compounds. Finally, we assessed the risk of the detected migrating substances.

2. Materials and Methods

2.1. Chemicals and Samples

Chemical standards of terfenadine and Val-Try-Val were from Sigma Life Science (St Louis, MO, USA), triallyl phosphite was from Alfa Aesar Thermo Fisher (Kandel, Germany), and sulfaguanidine, sulfadimethoxine, reserpine, caffeine, and acetaminophen were obtained from Sigma Aldrich (St Louis, MO, USA). Solutions of 10 ng/mL of these chemicals were prepared in H2O : MeOH (70 : 30, v/v) and used as internal standards.

Chemical standards of bis (2-ethylhexyl) adipate, camphor, dibutyl sebacate, dibutyl phthalate, erucamide, 2-(2′-hydroxy-5′-methylphenyl) benzotriazole (benazol P), methyl dihydrojasmonate, oleamide, and tributyl acetyl citrate (Citroflex-A4), all from Sigma Life Science (St Louis, MO, USA), and diethyl phthalate, dibutyl adipate, and tris(2,4-ditert-butylphenyl) phosphite (Irgafos 168), from LGC Standards (Bury, United Kingdom), were used to quantify and confirm the identity of the tentatively identified substances.

We analysed polycarbonate bowls that, according with the declaration of conformity, were used in repeated contact with miscellaneous foods such as soups and broths, during a maximum time contact of 2 hours and a temperature between 85°C and 89°C and prepared to endure until 2000 washing cycles.

2.2. Migration Test and Sample Preparation

Migration tests were achieved in agreement with the Regulation (EU) No. 10/2011 [1]. We used the food simulant C (20% of ethanol in water (v/v)). The migration test was performed during 2 hours at 100°C. We introduced around 200 mL of simulant into the PC rectangular bowl (10 cm × 5.5 cm × 3 cm) and keep it in the incubator. According with Regulation (EU) No. 10/2011, the migration test was repeated three times. Taking into account this Regulation, 6 dm2 is equal to 1 Kg of food.

2.3. LC-HRAMS Analysis

We used a Thermo Ultimate 3000 UHPLC system, with a column Hypersil Gold 100 mm × 2.1 mm × 1.9 µm (Thermo Scientific). The chromatographic system was linked with an Orbitrap ID-X Tribrid mass spectrometer (Thermo Fisher Scientific, USA). A volume of 5 µL was injected, and the flow rate was 300 µL/min. The chromatography started with 90% phase A (water) and 10% B (methanol). The linear gradient used was 0–18 min, 70% B; 18–21.5 min, 98% B; sustained at 98% B from 21.5 min to 25 min; decrease to 10% B, from 25 min to 26 min; and maintained in this initial conditions until 30 min.

Both positive and negative ionizations were employed. The H-ESI parameters were electrospray voltage of 3.5 kV positive (3.2 Kw negative), sheath gas of 25 arbitrary units (a.u), and auxiliary gas of 5 a.u. The ion transfer tube worked at 270°C and the vaporizer temperature at 180°C. A resolving power of 120.000 FWHM was used in full scan (100–900 m/z). The MS2 was acquired at 15.000 FWHM, with a precursor mass range of 125–900 m/z. The MS3 precursor was isolated in the quadrupole mass filter (0.4 Da), fragmented in the HCD cell and detected in the ion trap (FWHM ≤ 0.3).

2.4. Acquisition and Data Processing

For unknowns analysis, an intelligent data approach (AcquireX©, ThermoFisher Scientific) was employed. The details of this approach were described previously [19]. The acquisition workflows for Deep Scan (DS) and Interative Processing Exclusion (IPE) modes in DD-MS3 are shown in Figures SI-1-2.

For compound identification, the raw files acquired were processed using Compound Discoverer™ 3.1 (CD) (Thermo Fisher Scientific). The CD workflow is shown in Figure SI-3, and each node is defined in Table SI-1. The CD provides a wide list of annotated compounds (several hundreds). However, the majority of them do not present enough analytical evidence for tentative identification. To consider a compound tentatively identified with a high degree of confidence, we used the criteria previously described by [19]. In short, exact mass is with a Δ mass < 0.5 ppm; isotopic profile (SFit%) > 70%; MS2 match (experimental vs. library (mzCloud) spectra) > 70%; retention time consistent with their log P.

2.5. Safety Assessment

For safety assessment of the identified NIAS, we use the threshold of the toxicological concern (TTC) approach [2]. This was performed using the Toxtree software (http://toxtree.sf.net/predict) developed by Idea Consult Ltd., commissioned by JRC Computational Toxicology and Modelling (https://apps.ideaconsult.net/data/ui/toxtree). The software estimates the TTC following Cramer rules, and for each of the three Cramer classes, a tolerable daily intake (TDI, mg/person/day) is assigned. Class I, the least toxic class, has a TDI = 1.8 mg/person/day, Cramer class II (intermediate) has a TDI = 0.54 mg/person/day, and Cramer class III (most toxic) has a TDI = 0.09 mg/person/day.

The estimated daily intake (EDI) was calculated based on the default assumption in Europe that an adult person consumes 1 Kg of food packaged in a dm3, using the following formula [20].

EDI (mg/person x day) = migration (mg/kg) x 1 kg (food intake per person and day).

Quantification was performed using pure standards (Section 2.1). When standards were not available, a semiquantitative estimation of the migration (mg/Kg) was performed with the average response factor of seven internal standards [21] (Table SI-2).

Figure 1 shows the diagram of the overall analytical procedure.

3. Results and Discussion

3.1. Identification of Unknowns

Out of 727 annotated features with CD, only 24 meet the metrics established for tentative identification of compounds (Table 1). In order to achieve a high degree of identification confidence, very demanding criteria were followed (Section 2.5). All of them present a mass error (ΔM) in general lower than 0.5 ppm. Equally, the isotopic patterns present, in general, a SFit% > 70%. Likewise, their MS2 spectra match (>70%) with the spectra in the mzCloud library (Table 1). As an orthogonal criteria for increasing the identification confidence, the experimental retention time (Rtex) was compared with the theoretical one (Rtth). To estimate the theoretical retention time, we build a curve that relates the log P with the Rt of 107 substances of a wide range of polarities (Figure SI-4). Using this curve, we estimated the Rtth of the identified substances. In general, the Rtex (min) fits well with the Rtth (Table 1).


Compounda,b (CAS number)StructureΔ mass (ppm)Isotopic pattern (SFit%)MS2 matchcRtexp (min)Rttheo (min)MS3 matchdDescription [Reference]

3, 5-Ditert-butyl-4-hydroxybenzaldehydea,b (1620-98-0)−0.12887518.5418.26(1) CD in silicoMetabolite of antioxidant butylated hydroxytoluene (BHT) [22]

4-tert-Butylcyclohexyl acetatea,b (32210-23-4)0.055271.620.4016.72mzCloudFragrance [23, 24]

Benazol P(2-(2′-hydroxy-5′-methylphenyl)benzotriazole)a,b (2440-22-4)−0.01738919.3816.84mzCloudUltraviolet light absorber [1, 25]

Benzyl octyl adipatea,b (3089-55-2)0.349189.421.5823.48(1) CD in silicoPlasticizer

Bis (2-ethylhexyl) adipatea,b (103-23-1)−0.087363.822.56-mzCloudPlasticizer [26]

D,L-Camphora,b (76-22-2)−0.127175.616.1413.04Fragrance [27, 28]

Citroflex A-4a,b (tri-n-butyl acetyl citrate) (77-90-7)−0.028591.419.3423.40(2)Plasticizer [29]

Dibutyl hexanodioatea,b (dibutyl adipate) (105-99-7)0.115679.319.2916.94(1) CD in silicoPlasticise [30]

Dibutyl phthalatea,b (84-74-2)−0.267593.915.4518.41mzCloudPlasticizer [29]

Dibutyl sebacatea,b (109-43-3)0.038272.721.621.88(1) CD in silicoPlasticizer [29]]

Diethyl phthalatea (84-66-2)−0.085581.911.5512.02(1) CD in silicoPlasticizer [31]

Dodecyl sulfatea,b (151-21-3)−1.455594.622.9020.13(2)Surfactant [39, 40]

Dipentyl phthalatea,b (131-18-0)0.089370.921.0021.64(1) CD in silicoPlasticizer [41]

Erucamidea,b (112-84-5)0.39693.222.93mzCloudSlip promoter [1, 29, 42]

Galaxolidonea,b (507442-49-1)0.198972.919.9620.46(1) CD in silicoMetabolite of galaxolide, a polycyclic musk [43]

Hexadecanamidea,b (629-54-9)−0.4270.591.221.9624.50(1) CD in silicoSlip agent [42]

Irgafos 168a,b (tris(2,4-ditert-(butylphenyl) phosphite) (Phosphorous acid, tris(2, 4-di-tert-butylphenyl)ester) (31570-04-4)0.437487.525.10(1) CD in silicoAntioxidant stabiliser [1, 29, 44]

Methyl dihydrojasmonatea,b (24851-98-7)−0.147377.316.1411.92(1) CD in silicoFragrance [45, 46]

N,N′-Dicyclohexylureaa,b (2387-23-7)−0.02966214.7912.94mzCloud

DEETa,b (N,N-diethyl-m-toluamide) (134-62-3)−0.099377.313.1410.01(1) CD in silicoBiocide (repelling or attracting pests)

Octyl decyl phthalatea,b (119-07-3)−0.247993.622.87mzCloudPlasticizer [31]

Oleamidea,b (301-02-0)−0.068886.721.5625.20mzCloudSlip agent [1, 42]

Palmitoyl ethanolamidea,b (544-31-0)0.038171.721.3223.93mzCloudAntistatic; viscosity controlling [31]

Stearamidea,b (octadecanamide) (124-26-5)0.055296.922.4424.08mzCloudSlip promoter [1, 29]

aDetected with the AcqX_DS mode. bDetected with the AcqX IPE mode. aAll compounds present a full match for a predicted composition (molecular predicted composition from libraries from the experimental exact) mass; Δ mass (ppm), mass accuracy. bAll compounds have acquired MS2 and MS3 spectra (except MS3 for L-camphor). cMatch between the experimental and the MS2 spectra in the mzCloud library. Isotopic pattern (SFit%), match between the experimental isotopic pattern and the theoretical one; m/z Logic, a data analysis algorithm that combines the millions of available structural databases with the extensive mass spectral fragmentation library of mzCloud to rank order putative structures for unknowns when there is no direct mass spectral match; Rtexp, experimental retention time; Rttheo, theoretical time bases on log P. dMatch between the experimental MS3 and the database MS3 spectra (mzCloud) or the in silico fragmentation (Mass Frontier/CD); mzCloud, MS3 experimental spectra match with mzCloud spectra; CD in silico, match between the in-silico fragmented with the CD and the experimental MS3, (1) mzCloud does not contain a MS3 spectra of this compound and (2) the experimental MS3experimental do not match with that stored in mzCloud or the in silico fragmentation (Mass Frontier/CD).

For identification of those substances that do not meet the established criteria (only the molecular formula was provided by CD), a more in-deep and time-consuming manual examination is required, using in silico fragmentation tools and bibliographic examination [12].

In previous published studies for non-target screening applied to FCM, acquisitions using the data-dependent approach (DDA) with Q-Orbitrap and data-independent approach (DIA) with Q-TOF-MS instruments have been used [12]. The identification strategy is performed manually utilizing lists of probable candidates (only formula available), spectral libraries (MS/MS2 spectra), and bibliographical search. The main drawback of this strategy is that it is labour-intensive, and only a few compounds are tentatively identified. Regarding PC food materials, only a few substances migrating to simulants have been described. As mentioned previously, Bignardi et al. [13] and Bignardi et al. [14] performed a targeted and untargeted suspect screening to identify substances migrating from food contact polycarbonate using DDA-MS2 acquisition. The identification of compounds was carried out using a list of additives (target) and through the careful observation of the full scan chromatograms, the evaluation of the isotopic pattern, and the investigation in available databases. In the untargeted analysis, they claim the identification of several organic colorants and polycarbonate degradation products, but no MS2 spectra were used for structural identification. Another study [6] investigated, using a target method with LC-HRMS, the presence of the PC monomer bisphenol A (BPA) and several additives in polycarbonate tableware. BPA was determined in all samples (in the range of 0.5–6 µg/Kg), and the UV absorbers Cyasorb UV 5411, Tinuvin 327, and Tinuvin 324 and the whitening Uvitex OB were found in some samples (from 7 ng/Kg to 4460 ng/Kg). The target analysis, in general, permits achieve lower LOQ.

3.1.1. MS3 Spectra

The automated identification achieved by the combination of the intelligent data acquisition (AcqX-ddMS3) combined with the data processing using CD does not use the MS3 spectra. A higher level of confidence could provide the MS3 spectra. As can be seen in Table 1 and Table SI-3, all compounds identified have their MS3 acquired spectrum, except for D,L-camphor. However, it is necessary to compare the experimental and the library (mzCloud) MS3 spectra manually. For those compounds that do not have MS3 spectra in mzCloud, we fragmented them in silico using CD and Mass Frontier 8.0. [32].

Ten of the identified compounds had MS3 spectra that matched with that stored in spectrum library. Figure 2 shows, as an example, the spectra of benazol P and stearamide. In both MS3 spectra, the experimental parent ions (m/z 183.0679; m/z 130.1222, respectively) and the main fragments (m/z 155.06 and m/z 88.02, respectively) match with the library spectra. Must be taken into account that MS3 was acquired in low resolution. On the other hand, there are eleven substances in which experimental MS3 spectra match with the in silico fragmentation performed with the CD. As an example, Figure 3 depicts the experimental spectra of the methyl dihydrojasmonate and benzyl octyl adipate and the in silico fragments assigned to each m/z.

Using the criteria proposed by Schymansky et al. [33], the tentatively identified compounds present a high level of identification confidence (level 2a: unambiguous matching with library data). The other annotated compounds (not discussed here), for which only the molecular formula o exact mass is known, only achieve levels 4-5 (low levels of identification confidence).

We have confirmed the identity of 12 out of 24 tentatively identified substances using standards (Section 2.1). The rest of substances were not available in our lab.

3.1.2. Description of Identified Compounds

In order to explain the presence in the polycarbonate plastic material of the identified compounds, we search for their nature and technological uses. Table 1 shows the functions of these compounds. Many of them are additives, mainly plasticizers and slip agents used in plastics. Additives are introduced into plastic to enhance the quality of the attributes required for their appropriate use. They improve their physical (mechanical, thermal, and durability) and chemical properties and aid with processing of polymers [34].

Plasticizers are additives used to provide flexibility and improve their process ability, and between them, orthophthalates are the most used plasticizers [35]. The typical amount range 10–70% (w/w). Among the identified substances are included four phthalates (DEP, DBP, DPP, and ODP). Both DBP and DPP are included in the “Authorisation List” of Annex XIV of REACH [36] for their toxic effects for reproduction. However, DBP are listed in the Union List of the Regulation 10/2011 to be used as plasticizer in repeated use materials and articles contacting nonfatty foods with a specific migration limit (SML) of 0.3 mg/Kg (we have detected 1.34 mg/Kg). Contrarily, neither DEP nor DPP and ODP are in the Union List. Two other plasticizers such as Citroflex A-4 and bis (2-ethylhexyl) adipate are also included Union List of authorized substances (R. 10/2011).

Another group of identified substances is the slip agents, which reduce friction during and after plastic manufacturing and are used in the range of 0.05–3% (w/w) [37]. Oleamide, erucamide, stearamide, and hexadecanamide are authorized substances to be used as additives in plastics (IAS).

Antioxidants and ultraviolet stabilizers are widely used additives in plastics, usually in the range of 0.05–3% to enhance the lifetime of polymeric material, avoiding the oxidation process by oxygen or UV light [34, 37]. Benazol P is a benzotriazole ultraviolet (UV) light absorber that provides UV protection to a wide variety of polymers, including polycarbonates. It is an authorized substance included in the Union List, with a total specific migration limit (SML-T) of 30 mg/Kg for the restriction group of the benzotriazole-type UV stabilizers (three substances). Irgafos 168© is a phosphite antioxidant that provides polymers protection against thermooxidative degradation and is used in small amounts, usually between 0.004% and 0.5% [29]. It is included in the Union List (IAS).

We have also identified four odorants, which are added into plastics to add desirable fragrance or to mask any undesirable odor. 4-tert-Butylcyclohexyl acetate and methyl dihydrojasmonate are included in the EU cosmetics database [24] as perfumes. D,L-camphor is used as flavouring substance in foods and for perfuming industrial products [38]. On the other hand, galaxolidone is a metabolite of galaxolide, a polycyclic musk widely used as a fragrance in personal care and consumer products.

To our knowledge, these substances have not been previously determined in the polycarbonate food contact material. In a posterior target analysis using a target LC-MS/MS method, we determined BPA with concentrations ranging from 0.002 mg/Kg to 0.008 mg/Kg (details not provided). These low levels are difficult to detect with the wide scope of the untargeted methods.

3.2. Safety Assessment

For FCM, it is mandatory to guarantee their safety regarding the IAS and NIAS migration. For IAS, the migration concentration should be compared with the specific migration level (SML), established in the Regulation 10/2011. For those authorized substances with no SML, we have used the limit of 60 mg/Kg food (limit for overall migration).

For NIAS with toxicological reference values (TDI), we use this as a threshold (Table 2). For the rest of identified compounds, we applied the TTC approach described previously (Section 2.5).


SubstanceMigration concentration (mg/kg food)SML (mg/kg food)EDI (mg/person/day)Cramer classTDICramer (mg/person/day)TDI (mg/person/day)HQ (EDI/TDI)

3,5-Ditert-butyl-4-hydroxybenzaldehyde (1620-98-0)10.130.1320.540.24
4-tert-Butylcyclohexyl acetate (32210-23-4)10.130.1320.540.24
Benazol P (2440-22-4)20.07300.07
Benzyl octyl adipate (3089-55-2)10.040.0411.80.02
Bis (2-ethylhexyl) adipate (103-23-1)20.56180.56
D,L-Camphor (76-22-2)20.03600.03
Citroflex A-4 (77-90-7)20.03600.03
Dibutyl hexanodioate (105-99-7)20.010.0111.80.006
Dibutyl phthalate (84-74-2)20.210.30.210.6a0.35
Dibutyl sebacate (109-43-3)20.09600.09
Diethyl phthalate (84-66-2)20.010.0149.2b0.0002
Dodecyl sulfate (151-21-3)10.200.230.092.22
Dipentyl phthalate (131-18-0)10.050.0511.80.03
Erucamide (112-84-5)20.34600.34
Galaxolidone (507442-49-1)10.140.1430.091.56
Hexadecanamide (629-54-9)11.2251.22
Irgafos 168 (31570-04-4)20.99600.99
Methyl dihydrojasmonate (24851-98-7)20.020.0220.540.04
N,N′-Dicyclohexylurea (2387-23-7)10.020.0230.090.22
DEET (134-62-3)10.030.0330.090.33
Octyl decyl phthalate (119-07-3)12.442.4411.81.36
Oleamide (301-02-0)20.04600.04
Palmitoyl ethanolamide (544-31-0)10.030.0330.090.33
Stearamide (124-26-5)10.33600.33

1Migration (mg/kg) estimated semiquantitatively using the average response factor of a set of internal standards. 2Migration (mg/kg) calculated quantitatively using the calibration curve of the substance standard. Group restriction (sum of substances group restriction 12). Regulation 10/2011. Limit of 60 mg/kg for authorized substances (IAS) with no SML. Regulation 10/2011. Group restriction (sum of substances group restriction 32). Regulation 10/2011. aEFSA TDI 0.01 (mg/kg bw/day) [47]. Calculation of TDI in mg person−1 day−1 considering a person’ weight of 60 kg. bUS EPA TDI 0.8 (mg/kg bw/day) [48]. Calculation of TDI in mg person−1 day−1 considering a person’ weight of 60 kg.

The IAS benazol P, bis (2-ethylhexyl) Citroflex A-4, and hexadecanamide present a migration concentration lower than the established SML; therefore, their exposures are not of concern (Table 2). None of the authorized substances without SML exceeds 60 mg/Kg food. The rest of the identified substances show a HQ < 1; consequently, their migration does not represent a risk. The HQ is not a regulated limit but a risk metric.

More in-deep investigation is needed to uncover the identity of all annotated but not identified substances and to perform a risk assessment.

4. Conclusions

A new and automated analytical strategy for identification of unknown substances in food contact materials was applied to food contact polycarbonate and permitted the identification of 24 substances, mainly plasticizers, slip agents, and antioxidants. The majority of these substances have not been previously identified in PC food contact materials.

The use of the intelligent data acquisition (AcquireX©) in both modes (DE and IPE) has permitted a fast and exhaustive data acquisition, and the use of DDA-MS3 provides profuse structural information that increase the identification confidence.

The implementation of an automated workflow for database searching is essential to avoid labour intensive and time-consuming explorations. The use of a specific CD workflow has permitted a very fast search in different databases, which could be improved increasing the database content with more substances.

We have defined very rigorous criteria for identification of the annotated substances, in order to provide to the analytical strategy with a high level of identification confidence. The use of MS3 provides more structural information that increases this confidence. However, some general accepted guidelines for NIAS identification are necessary.

4.1. Study Limitations

For several identified substances, a semiquantitative migration (mg/kg) was estimated using the average response of seven internal standards not chemically related with the identified substances. This, obviously, is a rough approximation for risk assessment that could be improved using the standards of the identified substances.

Data Availability

The data used to support the findings of this study are available from the corresponding author upon request.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

Acknowledgments

The study was performed using analytical instruments financed by the European Commission through the European Regional Development Funds (ERDF) Operational Programme of the Valencia Region (2014–2020). Pablo Dualde acknowledges his “Ayudas para la contratación PTA” (PTA2018-016320-I) from “Ministerio de Ciencia e Innovación” (Spain).

Supplementary Materials

The Supplementary Materials include the following Figures and Tables: Figure SI-1. Workflow for the ddMS3 used in the AcquireX Deep Scan mode. Figure SI-2. Workflow for the ddMS3 used in the AcquireX IPE mode. Figure SI-3. Compound discover workflow. Figure SI-4. Log P and retention time (Rt) of the quality control compounds. Table SI-1. Description of the different nodes of the CD workflow. Table SI-2. Calculation of the average response factor. Table SI-3. Experimental MS3 transitions. (Supplementary Materials)

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