Recent Advances in Non-Targeted Screening of Compounds in Plastic-Based/Paper-Based Food Contact Materials
Abstract
:1. Introduction
2. Separation, Extraction, and Migration Experiments of Chemical Substances in Plastic/Paper-Based FCMs
2.1. Separation and Extraction of Chemical Compounds in Plastic/Paper-Based FCMs
2.2. Migration Experiment
2.3. Recent Developments and Applications of Migration Experiments
3. NTS MS Analysis of Compounds in Plastic/Paper-Based FCMs
3.1. TOF Compares Orbitrap and Its Application Instance
3.2. Application of LC-HRMS Technology in FCM Detection
3.3. The Development of LC-HRMS Combined with Computer Algorithms and Metrology Methods
3.4. Application of GC-HRMS Technology in FCM Detection
3.5. Development of Full Two-Dimensional Meteorological Chromatography (GC × GC)-HRMS for NTS Detection of FCMs
3.6. Development of Analytical Methods for GC-HRMS
4. Conclusions and Prospects
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
Abbreviations
ASE | accelerated solvent extraction |
APGC | Atmospheric-pressure gas chromatography |
ASAP | Ambient solid analysis probe |
BP | benzophenone |
BFRs | brominated flame retardants |
EI | electron impact |
FCM | food contact material |
GC | gas chromatography |
GC × GC | full two-dimensional meteorological chromatography |
GC-MS/MS | gas chromatography-tandem mass spectrometry |
HRMS | high-resolution mass spectrometry |
HS | headspace extraction |
HS-SPME | headspace solid-phase microextraction technology |
IMS | ion mobility spectroscopy |
LC | liquid chromatography |
LDPE | low-density polyethylene |
LLE | liquid–liquid extraction |
LPME | Liquid-phase microextraction |
MAE | microwave-assisted extraction |
MHS-SPME | multi-headspace solid-phase microextraction technique |
MOAH | Mineral oil aromatic hydrocarbons |
MS | mass spectrometry |
NIAs | non-intentionally added materials |
NTS | non-targeted screening |
PA | polyamide |
PAAs | Primary aromatic amines |
PAPs | polyfluoroalkyl phosphate |
PE | polyethylene |
PET | polyester |
PFCAs/PFSAs | Perfluorocarboxylic acid/sulfonic acid |
PFAs | Polyfluoroalkyl substances |
PTOHs | fluoropolyols |
qTOF | quadruply-time-of-flight |
rPET | recovered polyethylene terephthalate |
RSD | relative standard deviation |
SPE | solid-phase extraction |
SPME | solid-phase microextraction |
SVOCs | semi-volatile organic compounds |
TOF | time of flight |
UAE | ultrasound-assisted extraction |
UPLC | ultra-performance liquid chromatography |
VCs | volatile contaminants |
VOCs | volatile organic compounds |
2,4-DTBP | 2,4-di-tert-butylphenol |
2-BP | 2-hydroxybenzophenone |
4-BP | 4-hydroxybenzophenone |
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Type | Extraction Method | Advantage | Disadvantage | Typical Example | Reference | |
---|---|---|---|---|---|---|
Extraction technology of volatile and semi-volatile compounds | HS | Simplify your pre-treatment and avoid organic solvents, the most simple and commonly used, suitable for GC and ion migration spectrometry | The extraction effect is limited due to the low air pressure and slow mass transfer | Utilizing HS-gas chromatography mass spectrometry (GC-MS) and multivariate statistical analysis, Chen et al. were able to differentiate between primary and recycled polyethylene (PE). Their findings revealed 47 volatile organic compounds (VOCs) within four categories, including aliphatic hydrocarbons and additives. Through the use of orthogonal partial least squares discriminant analysis and non-parametric tests, they successfully identified 16 VOC markers. | [18,19,20] | |
Purge and capture technique | Has high sensitivity, good enrichment effect, and high upper boiling point, which is conducive to the detection of trace analytes | Easy to form foam, easy to overload the instrument, time-consuming, may introduce impurities, universal adsorbent selection is difficult | Ibarra et al. used purge and capture technology combined with GC-MS to analyze VOCs and semi-volatile organic compounds (SVOCs) in organic solvent extracts from 12 plastic packaging materials, detecting approximately 100 different compounds. | [21,22,23] | ||
Headspace solid-phase microextraction technology (HS-SPME) | It can extract VOCs and SVOCs easily and without solvents, while also handling sample collection, concentration, injection, and analysis | Extracting weak volatile components is challenging due to interference from experimental conditions | Parigoridi et al. studied methods to separate plasticizer mixtures from recycled paperboard for food packaging and developed a technique to detect low concentrations of comparable chemicals. | [24,25,26] | ||
Multi-headspace solid-phase microextraction technique (MHS-SPME) | Trace analysis is more sensitive, matrix effects are gone, accurate quantification results and multiple analytes can be quantified without external calibration. | Headspace saturation needs to be avoided | A study by Salazar et al. analyzed VOCs in polylactic acid particles and identified aldehydes, ethanol, and acetone using MHS-SPME. They also found three specific compounds: acetaldehyde, 2-methyl-2-propanol, and 2,3-pentanedione. | [27,28] | ||
Extraction technology of non-volatile compounds | Solid–liquid extraction combined with field-assisted extraction technology | Microwave-assisted extraction (MAE) | Ensure efficient energy transfer, minimize solvent use, shorten extraction time. | The reaction cycle is lengthy and the operational process is complex | A study conducted by Moreno-Gordaliza et al. analyzed the potential migration of silver ions and microplastics in antibacterial food plastic containers during regular use and microwave heating. The results revealed that in certain scenarios, the migration levels surpassed the acceptable limits of risk. | [29,30] |
Ultrasound-assisted extraction (UAE) | Efficient and simple extraction with low instrument threshold for good results | Sample damage from ultrasonic attenuation makes control and handling difficult. | A review by Peters et al. looked at ways to detect non-intentionally added materials (NIAs) in paper-based FCMs. Methods included UAE for extracting NIAs. | [17,31] | ||
Accelerated solvent extraction (ASE) | Efficient extraction with minimal solvent and low impact on the body | High equipment requirements | Dorival-Garcia et al. used ASE optimization and LC-HRMS to identify over 100 additives and degradation products in multilayer polymer systems of disposable plastic bags. | [32,33,34] | ||
The QuEChERS method | FCM impurity purification requirements can be met with this fast, simple, economical, effective, stable, and safe option | The QuEChERS method needs improvement to detect complex FCMs | Diamantidou et al. developed an ultra-high-pressure liquid chromatography(UPLC)-quadruply-time-of-flight (qTOF) mass spectrometry (MS) method for the analysis of NIA migration in FCMs, olive oil, and food simulants in different saturated polyester (PET) bottles. | [35,36,37,38,39] | ||
Enrichment technology | Solid-phase extraction (SPE) | Flexible and diverse, high sensitivity, good reproducibility, can be set sampling, extraction, concentration, sampling in one | The cost is high, the method development is difficult, and it is not suitable for solid samples | Liu et al. established a pipette tip SPE combined with HPLC and photodiode array detector for the detection of atomic absorbents in polyamide (PA) FCMs for migration detection of six atomic absorbents in PA kitchenware. | [40,41,42,43,44] | |
Liquid–liquid extraction (LLE) | Simple and fast operation, high selectivity, no special equipment required | Extracting water-soluble compounds from water is tough due to the high organic solvent content and long operation time. | Tsochatzis et al. has developed and refined the salt-out LLE technique to analyze caprolactam and 2,4-di-tert-butylphenol (2,4-DTBP) in water and food simulant samples. The method achieved high accuracy with recovery rates of 87% and 95%, respectively, and a relative standard deviation (RSD) below 12%. | [45,46,47] | ||
Solid-phase microextraction (SPME) | Easy to operate, efficient and sensitive, can selectively enrich compounds, small sample size | May be affected by interference, selectivity and sensitivity are affected by the sample and solid-phase material | Li et al. utilized oxygenated carbon nanotube cage materials, which were created by oxidizing zeolite imidazole-frame-67, as SPME packages for extracting aromatic amines from FCMs. And they developed a new detection method with gas chromatography-tandem mass spectrometry (GC-MS/MS). | [48,49,50,51,52,53,54,55] | ||
Liquid-phase microextraction (LPME) | Simple operation, high enrichment efficiency, small extractant dosage, easy to combine with chromatographic system | Extraction solvent, temperature, salt, pH, and stirring affect it easily. | Li et al. designed eight novel low-viscosity hydrophobic eutectic solvents as extractants for eddy-assisted LLME technology to extract and preen rich phthalates from water samples, and determined phthalates content in plastic FCMs using GC-MS. | [56,57,58,59,60] |
Number | Sample | The Migrants | Food Simulants | Research Content | Reference |
---|---|---|---|---|---|
1 | Spike paper | Photoinitiators such as benzophenone (BP), 2-hydroxybenzophenone (2-HBP) | Tenax®, Porapak®, and Tylose® | The migration behavior of Porapak® was similar to that of Tenax®, but Tylose® was slightly lower in the order of 2HBP > BP > 4-hydroxybenzophenone (4-HBP) among all simulants, with the migration amount of 4-HBP significantly lower. | [66] |
2 | Multilayer PA packaging | ε-caprolactam | Water, 3% acetic acid solution, olive oil | At high temperature and atmospheric pressure, ε-caprolactam migrates more to different simulants than at high pressure, but remains below the permitted specific migration value of 15 mg/kg. | [67] |
3 | Primary carton packaging | Mineral oil aromatic hydrocarbons (MOAHs) | Modified polyphenoxyethylene | The migration patterns of model compounds are influenced by their volatility and food substrate. The behavior of the most volatile and heaviest compounds is distinctive. | [68] |
4 | Plastic FCMs | Antioxidant | 95% ethanol, water, and 4% acetic acid | Irganox 1010, Irganox 1076, and antioxidant LTDP had the highest detection frequency and concentration | [69] |
5 | Paper FCMs | Mineral oil hydrocarbons | Tenax® | The maximum temperature of Tenax® in paper-based FCMs migration testing should not be higher than 40 °C. | [70] |
6 | Water | Primary aromatic amines (PAAs) | Water; 3% acetic acid; 10%, 20%, and 50% ethanol | PAAs is most unstable in 3% acetic acid and more stable in 3 mmol/L HCl solution. In ethanol-containing food simulants, most PAAs are stable. Reducing the temperature can improve its stability, and shortening the storage time can improve its recovery rate. | [71] |
7 | Paper FCMs | Perfluorocarboxylic acid/sulfonic acid (PFCAs/PFSAs), polyfluoroalkyl phosphate (PAPs), and fluoropolyols (FTOHs) | 20%, 50% ethanol | Migration of PFCAs and FTOHs to 50% ethanol is higher than migration to real food, while FTOHs do not migrate to 20% ethanol. Children’s estimated dietary exposure to polyfluoroalkyl substances (PFASs) is exceeding the safe threshold and poses a health risk. | [72] |
8 | Paper and cardboard materials | Photoinitiators, phthalates and plasticizers | 50%, 95% ethanol, and Tenax | Tenax was an adequate simulation model for the migration to rice and cereals, but underestimated the migration to infant milk powder, 95% ethanol was a superior simulant for this particular food | [73] |
9 | Paper and board materials | Per- and polyfluorinated compounds | 50% ethanol, 95% ethanol, and Tenax® | Tenax®-based techniques underestimate the migration of PFASs to food stuffs, particularly for short-carbon-chain PFASs and milk powder. | [74] |
10 | Contaminated food contact articles | Brominated flame retardants (BFRs) | Water, 3% acetic acid, 10% ethanol and 50% ethanol | HBCD not detected. Phenolic BFRs (tributyl phosphate and tetrabromobisphenol A) migrated in food simulants from nondetected to 73 µg/kg, and in foods from 1 to 23 µg/kg. Phenolic BFRs migrated more into 50% ethanol than aqueous simulants and foods. | [75] |
11 | Bio-based food packaging material | Brominated flame retardants | 96% ethanol | Real samples had low chemical migration in most cases, except for one case. Low percentage suggests low health concern. | [76] |
Number | Sample | Screened Compound | Instrumental Method | Detection Limit/ Quantification Limit | Detected Quantity | Recovery | Reference |
---|---|---|---|---|---|---|---|
1 | FCMs | 11 PFAS | UPLC- IMS-QTOF | 0.07~3.42/0.20~11.4 μg/kg | 3.2~22.3 μg/kg | 119 ± 22% | [81] |
2 | FCM extract | 64 small-molecule compounds | UPLC-QTOF-MS | — | 0.0001~14.2470 mg/d | — | [93] |
3 | Liquid food simulator, PA/PE FCM multilayer film | 13 PA monomers and oligomers | QTOF-MS | 0.6~4.8/1.7~14.5 μg/L | 18.1~212.2 ng /mL | 78.3%~108.7% | [94] |
4 | Plastic FCMs for microwave and conventional oven heating | 74 kinds of migration compounds | LC-Orbitrap-MS | — | — | — | [95] |
5 | Juice milk bag, 18 kinds of packaging samples | 10 kinds of UV ink photoinitiator and 8 kinds of PAAs | LC-Orbitrap-HRMS | —/0.5~5µg/kg | 0.004~658 ng/g | 72%~120% | [96] |
6 | Envelope | 22 kinds of plasticizers | UPLC-MS | 0.04~10/1.0~50 μg/kg | — | 75.6~124.5% | [98] |
7 | FCM UV varnish | 54 kinds of NIAs | UPLC-ion mobility-QTOF-MS | 0.01~0.1/— mg/kg | 0.01~3.83 mg/kg | — | [99] |
Number | Sample | Screened Compound | Instrumental Method | Detection Limit/ Quantification Limit | Detected Quantity | Recovery | Reference |
---|---|---|---|---|---|---|---|
1 | Plastic FCMs for microwave and conventional oven heating | 74 kinds of migratory compounds | GC-Orbitrap-MS | — | — | — | [95] |
2 | Polypropylene-based FCMs | 27 kinds of VOCs, SVOCs | APGC-QTOF-MS | — | — | — | [103] |
3 | FCMs | 27 best markers of MOAH | Ambient solid analysis probe (ASAP)/APGC-QTOF-MS | 0.01~0.06/0.1~0.3 μg/g | 8.62~25.12 mg/kg | — | [104] |
4 | Paper FCMs | 35 kinds of migratory compounds | GC-Orbitrap-MS | — | 189~600 μg/kg | — | [105] |
5 | Polylactic acid and PET blend | 15 kinds of VOCs | APGC-QTOF-MS | 226~2800/310~8400 µg/kg | — | 40.0%~91.3% | [106] |
6 | Water | 12 neutral PFAS substances | HS-SPME-GC-atmospheric pressure-photoionization-HRMS | 0.02~0.24/0.08~50 ng/L | — | — | [107] |
7 | Polypropylene FCMs | 45 kinds of VOCs, SVOCs | GC-electron impact (EI)-QMS/GC-EI-TOF-MS | — | 5.4%~98.9% | — | [108] |
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Chen, Y.; Li, H.; Huang, H.; Zhang, B.; Ye, Z.; Yu, X.; Shentu, X. Recent Advances in Non-Targeted Screening of Compounds in Plastic-Based/Paper-Based Food Contact Materials. Foods 2023, 12, 4135. https://doi.org/10.3390/foods12224135
Chen Y, Li H, Huang H, Zhang B, Ye Z, Yu X, Shentu X. Recent Advances in Non-Targeted Screening of Compounds in Plastic-Based/Paper-Based Food Contact Materials. Foods. 2023; 12(22):4135. https://doi.org/10.3390/foods12224135
Chicago/Turabian StyleChen, Ya, Hongyan Li, Haizhi Huang, Biao Zhang, Zihong Ye, Xiaoping Yu, and Xuping Shentu. 2023. "Recent Advances in Non-Targeted Screening of Compounds in Plastic-Based/Paper-Based Food Contact Materials" Foods 12, no. 22: 4135. https://doi.org/10.3390/foods12224135
APA StyleChen, Y., Li, H., Huang, H., Zhang, B., Ye, Z., Yu, X., & Shentu, X. (2023). Recent Advances in Non-Targeted Screening of Compounds in Plastic-Based/Paper-Based Food Contact Materials. Foods, 12(22), 4135. https://doi.org/10.3390/foods12224135