band 50,
April 2016
, pp. 118-130
Author link opens overlay panel, ,
Abstract
background
The variety of food and beverage packaging has increased in recent years due to the development of new plastic materials and (co)polymer modifications. Oligomers, which are always present in polymers, have attracted qualitative and quantitative attention as potential migrators.
scope and method
This article considers oligomers as potential migrants from plastic food contact materials and outlines their occurrence and analytical methods for identification and quantification. In addition, the section on migration summarizes the literature on food simulants and oligomer levels in foods. Particular attention is paid to condensation polymers, as these represent a rapidly growing area of polymers due to the increasing number of EU-approved (co)monomers.
Key Findings and Conclusions
When evaluating the oligomer content and migration potential of a polymer, several factors must be considered, such as separation of oligomers from the material, selection of appropriate separation and detection techniques for identification and quantification, and selection of appropriate standards. In general , the mass spectrometry technique is coupledLiquid ChromatographyThey have been shown to represent the analytical method of choice. To the best of the authors' knowledge, this is the first review of analytical methods focusing exclusively on oligomers as polymer-specific substances, suggesting that they should be considered as separate polymer-related and polymer-type-specific groups of added substances (NIAS) as well as So-called unintentional substances.
introduce
The use of plastic has increased steadily since its discovery. In 2013, packaging applications accounted for the largest portion of plastic use in Europe (Plastic Europe, 2014). The most commonly used polymers for such applications are PE, PP, PET, PS and PVC. In the past, the starting molecules for plastics were mainly based on petrochemicals. Today, however, people are looking for alternative plastic monomer units that can be produced from renewable resources such as plants. For reasons of environmental protection, biodegradability is also considered when developing new polymer packaging materials.
Over the past five years, the variety of food and beverage packaging has increased due to the development of new plastic materials and (co)polymer modifications. An inherent consequence is that oligomers, which are always present in polymers, are not only quantitatively but also qualitatively of concern as potential migratory species. An increasing number of new comonomers automatically increases the number of possible oligomeric structures in the composition.
Many requirements are placed on polymeric food contact materials (FCMs), such as physical protection of food from temperature, pressure and mechanical shock, as well as barrier protection against oxygen, water vapor and dust. Additionally, plastic FCMs are said to protect products from bacterial contamination, viruses, mold and fungus, ensuring long-lasting quality and safety. On the other hand, food contact materials can interact with the product. One of the processes involved is migration, the transfer of molecules present in the FCM to food. Migration of substances should not exceed permissible quantities as they pose a risk to consumers. European Regulation 10/2011/EU on plastic materials coming into contact with food lays down specific rules for safe use of plastic materials and articles (EU, 2011). A positive list is provided allowing the use of monomers, other starting materials and additives in the manufacturing process. These substances are known as intentionally added substances. Their specific or general migration restrictions are listed in Annex I to Regulation 10/2011/EU. Substances resulting from the degradation of polymeric materials or additives and impurities in the starting materials are unintentionally added and are not included in the authorization, as it would be impractical, if not impossible, to identify all impurities. These substances are commonly referred to as NIAS (Non-Intentionally Added Substances). For unapproved substances, the migration amount should not exceed 0.01 mg/kg food. However, this does not apply to substances that are carcinogenic, mutagenic or toxic to reproduction (CMR substances). Pay special attention to compounds with molecular weights up to 1000 Da. Due to their size, substances with higher molecular weight are generally considered to be physiologically non-absorbable. Nontargeted screening methods have been proposed for detection and identification of NIAS (Nerin, Alfaro, Aznar, & Domeño, 2013). However, quantification of NIAS is difficult due to the many existing chemical substance classes and their varying analytical detection capabilities and response factors. Today, identification of unknown compounds is often accomplished using high-resolution mass spectrometry (HRMS). This provides the exact mass of the substance, accurate to four decimal places, which is critical for identifying compounds. Current MS software programs can use the isotopic patterns recorded by the instrument to calculate possible chemical formulas for the measured masses. Probable chemical structures can be suggested using fragmentation experiments, sample knowledge, and database searches, such as Chemspider (www.chemspider.com) or Norman Public Bank (Public Bank.ufz.de).
When it comes to ingredients in food contact materials, oligomers are often classified as unintentionally added substances (Nerin et al., 2013). However, oligomers are inevitably formed during polymerization and thus can be considered as polymer-specific by-products. In fact, the pattern of oligomers formed is related to the polymerization process and can provide information about the type of polymer. They are not specifically regulated in Regulation 10/2011/EU and are therefore effectively in a legal "grey area". Due to industrial developments, the permanent extension of the EU Positive List to include new comonomers has essentially led to an exponential increase in the number of new oligomers that may be present as potential migrants in food contact polymers. Often, the identity and biological properties or toxicological profiles of oligomers are not fully understood. The same is true for the migration and exposure rates of packaged foods. Traditionally, oligomers have been rarely tested for toxicity and safety assessments are often based on toxicity data from monomeric units, e.g. assuming complete hydrolysis of oligomers (Nelson, Patton, Arvidson, Lee, & Twaroski, 2011). In general, however, little is known about the degradation of oligomers in the gastrointestinal system, so it may be necessary to evaluate oligomer structures individually as individual compounds or to study their hydrolysis.
Oligomers must be extracted from the polymer matrix using a suitable solvent prior to analysis. Furthermore, separation of the compounds present in the sample is critical for proper identification and quantification. This is usually done by on-line gas chromatography or liquid chromatography. The advantage of oligomers is that they are related to their host polymer, so the monomer units are well known. Therefore, the masses of theoretical oligomers can be calculated and searched directly in the mass spectrum, simplifying mass spectrometric identification. Detection methods other than or in combination with MS can be used, such as ultraviolet (UV), flame ionization (FI), evaporative light scattering (ELS), chemiluminescent nitrogen (CLN), and charged aerosol (CA) low Polymer. ). The problem here is the different reactions of the compounds in the analytical detector. Especially in the case of mass spectrometry detection, the reactions between molecules with different structural features can vary widely. It is generally assumed that a group of homo-oligomers have the same response factor. However, if possible, this should be verified using quantitative response detection methods such as UV.
In order to examine oligomers in detail, it is important to know which monomers each polymer is made of. The main analytical question and challenge is: how to identify oligomers present in food contact materials? How to quantify the amount of oligomers leached into food and beverages? How should the risk assessment be carried out? The aim of this review is to summarize the relevant literature and in this way provide answers to these questions in light of the current state of published scientific knowledge. This review focuses more on polycondensation polymers, which are increasingly used and proposed as new alternative food contact materials, rather than polyhydrocarbons, such as polyolefins formed by addition polymerization. These more polar and partially biodegradable polymers contain a large chemical diversity of oligomers that can be analyzed using modern LC-MS techniques.
Sectional view
Oligomers - Definition, Chemical Formation, Sources and Types
Oligomers (oligo=some - mers=parts) are defined as molecules consisting of a small number of monomer units. Depending on the chemical composition of the building blocks, they typically contain 2 to 40 repeating units. In general, species with a molecular weight below 1000 Da are considered as relevant potential immigrants (EU, 2014). Toxicological interest has focused on these substances because only these molecules are said to be absorbed from the gastrointestinal tract (Donovan, Flynn, and
Analytical method
Potential migration analysis of food contact materials is complex and demanding. Knowing the material composition and manufacturing process is an advantage. By examining the sample in detail, it is possible to determine which compounds are definitely present, such as monomers and additives. In addition, compounds that may arise from side reactions or degradation reactions can be detected. It is often difficult to obtain sufficient information about a particular sample. there are many
oligomer migration
Migration is the transfer of mass from food contact materials to food by physical processes. For reproducibility and analytical reasons such as possible ion suppression due to matrix interferences, migration was tested using a food simulant (EU, 2011). In addition, the test conditions such as time, temperature and test medium were also standardized. A distinction is made between specific migration, where only the migration of a single species or chemical group is measured, and overall migration
polymer additives
In order to obtain plastic materials more suitable for practical use, various additives are used. They protect polymeric materials from degradation caused by processing and manufacturing conditions, as well as exposure to sunlight, heat and oxygen, which can cause changes in properties such as color, barrier function and physical state. There are different classes of additives, which can also be polymeric or oligomeric. For example, hindered amine light stabilizers (HALS) protect
diploma
The identification and quantification of oligomers is an important issue for food safety due to (i) gaps in knowledge about the toxicological properties of oligomers and (ii) the increasing number of different (co)monomers used in the production of polymers. An increasingly relevant and analytically challenging task. In order to evaluate polymers in terms of oligomer content and migration potential, various factors such as separation of oligomers from the material, proper identification of oligomers, selective separation, etc.
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Chemicals and their hazards associated with plastic packaging - an overview
In 2023, the chemical layer
Plastic packaging contains residues of substances used in the manufacturing process, such as B. solvents, and unintentionally added substances (NIAS), etc. B. Impurities, oligomers, or degradation products. A search of the peer-reviewed literature revealed at least 10,259 chemicals associated with plastic packaging materials, including those used in manufacturing and/or contained in end-of-line packaging items. We then summarize and discuss their chemical structures, analytical tools, migration characteristics and hazard classes where possible. For plastic packaging chemicals, a literature review shows that gas chromatography and liquid chromatography are often combined with various high-resolution mass spectrometry-based precision mass analyzers in order to identify unknown migrated species in plastic packaging. Chemical migration from food packaging is influenced by several parameters, including the type and complexity of the food, contact time, system temperature, type of packaging contact layer, and the identity of the migrated species. A review of the specialized literature shows that information on adverse effects is only available for about 1600 substances. Of these, additives appear to be more toxic to wildlife and humans than monomers. Neurotoxicity accounted for the highest proportion of all chemical types, and benzene, organic acids and their derivatives were the most toxic chemical types. In addition, studies have shown that hydrocarbon derivatives, organonitrogen compounds, and organometallic compounds are the most dermally toxic, while organohalogen compounds are the most hepatotoxic. The main cause of skin allergies is organic salts. The research lays the groundwork for widespread dissemination of information about chemicals in plastics and contributes to a better understanding of their potential risks to the environment and humans.
Is the COVID-19 pandemic redefining the everyday food packaging materials industry?
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The COVID-19 pandemic has been a topic of conversation around the world as it has swept the world population and changed many aspects. The pandemic has directly or indirectly affected all sectors. The food industry took a direct hit. The food packaging industry has taken this opportunity to serve and feed those affected by the pandemic, but there have also been interactions, reactions and consequences throughout the course of the pandemic. The purpose of this perspective is to highlight the importance of the food packaging industry (from a COVID-19 perspective) and to highlight that food packaging materials are not ready for such times. Regardless, as the world is being asked to live with corona, improvisation is necessary, bugs in systems have to be fixed, and the entire packaging industry has to crunch to be able to live with corona or to face something much worse than corona worse. The purpose of this discussion is to understand the seriousness of the actual situation and process the information from the scattered fragments of the report. The use of food packaging materials generates a lot of plastic waste. Single-use plastics have become popular due to fears of contamination, leading to a massive turnover of waste. Due to the fear of corona, a large number of disinfectants and disinfectants are sprayed on the surface of food packaging materials to disinfect the surface. Food packaging is tailored to the needs of food containers and has never been used for sanitizing sprays. The consequences of these sanitation procedures are unprecedented, neglected, and no action appears to be taken in the post-COVID-19 phase. The coronavirus took us by surprise this time, but next time at least the food packaging industry needs to be well prepared. The speculative consequences are examined and sound recommendations are made. Emphasize the need for comprehensive research in this direction in soil reality studies.
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Quote excerpt:
In recent years, many researchers have begun to realize the food safety risks brought about by the migration of harmful substances in food contact materials. However, in practice, it is found that the composition of food contact materials is very complex [22-24]: in addition to the raw materials and various additives added in the manufacturing process, it also contains many impurities and reaction intermediates or decomposition products produced in the production process [ 25]. The sources of these substances are complex, their properties are unknown, and their contents are difficult to quantify, which poses a major challenge to the safety assessment and risk management of food contact materials.
A technique for the detection and control of cycloesterification (CE) in biodegradable polyesters is presented. It should be noted that CE can be extracted by extraction or migration and then detected by GC-MS or LC-MS depending on the volatility, LC-MS technique is more commonly used since CE is usually less volatile. CE has been detected in several typical biodegradable polyesters, such as polylactic acid (PLA), polybutylene succinate (PBS), and polybutylene adipate terephthalate with repeat units less than 10 Alcohol esters (PBAT); the improvement of the polymerization process and the use of organic solvents to wash biodegradable polyester particles can effectively reduce the CE content, and the washing strategy is relatively more convenient and efficient.
Review of the food safety evidence base and risk assessment for polyethylene terephthalate oligomers: a systematic evidence map scheme
2022, Environment International
Polyethylene terephthalate (PET) oligomers are commonly found in PET used in food contact applications. Migration of consumer exposure to PET oligomers into food and beverages has been documented. However, to date, there is no specific risk assessment framework or guidance for the safety assessment of PET oligomers.
The goal of this Systems Evidence Map (SEM) is to identify and organize existing clusters of knowledge and related gaps in hazard and exposure information for PET oligomers. Research needs were identified as input to the chemical risk assessment and to support future toxicity testing strategies and regulatory decisions for PET oligomers.
It searches multiple bibliographic databases (including Embase, Medline, Scopus, and Web of Science Core Collection), chemical databases (SciFinder-n, Reaxys) and gray literature sources, supplementing search results with properly documented forward and reverse reference tracking . The search was based on a single-concept PET oligomer-centric strategy to ensure sensitive and impartial collection of all evidence related to hazards and exposures in a data-poor setting. Scoping studies carried out during planning identified 34 relevant PET oligomers. Eligible entries of any study type must include primary study data on exposure, health or toxicological outcomes for at least one relevant PET oligomer.
For indexed scientific literature, titles and abstracts are screened by reviewers. Selected studies were thoroughly reviewed by two independent reviewers. Gray literature was reviewed for inclusion and exclusion by two independent reviewers.
No risk of bias analysis was performed as part of this SEM.
Conducted by one reviewer, indexed scholarly literature by a second reviewer, and gray literature by two independent reviewers.
The extracted and encoded information is synthesized in various formats, including narrative synthesis, tables, and heatmaps.
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Untargeted Screening of Polyester Phenolic Can Paint Extracts: Identification of New Aldehyde Molecules in Resole Resins
2022, talent
Phenolic and substituted phenolic resole resins are commonly used in the formulation of can coatings. However, migration analysis of these coatings has been poorly described compared to other coating techniques. While epoxies and polyesters are known to have migrations with established mechanisms of formation, unintentionally added substances (NIAS) specifically related to phenolic resins are rarely explored in the literature. The purpose of this publication is to further investigate the effect of resole resins used in can coating formulations on the properties of the extracted NIAS. Six different polyester phenolic can coating models were formulated with specific phenol, cresol or tert-butylphenol based resole resins. Can coating films were extracted in acetonitrile at 40°C for 24 hours prior to analysis. NIAS identification was performed using gas chromatographic separation coupled with high-resolution mass spectrometry (HRMS) and nuclear magnetic resonance spectroscopy (NMR). Cyclic polyester oligomers were found in all extracts at concentrations ranging from 10 μg/dm2Double 226μg/dm2, not specifically affected by the resole resin used in the formulation. While few or no peaks were observed for cresyl and phenol-based resoles, 48 were specifically observed in paint extracts containing tert-butylphenol-based resoles and their respective resole formulations peak. The strongest peaks were identified as aldehydes by HRMS and NMR analysis. These aldehydes were semiquantified in similar proportions as polyester oligomers. The presence of such aldehydes has never been reported in the literature on NIAS in can coatings. Further studies are then required to better understand the mechanism of aldehyde formation and to assess the toxicological profile of this class of chemicals.
Featured Articles (6)
research article
Accidentally Added Substances in Food Contact Materials: How to Ensure Consumer Safety
Current Opinion in Food Science, Band 6, 2015, S. 33-37
There is growing concern about the presence of unintentionally added substances (NIAS) in food contact materials. These substances cannot be excluded from food contact materials and end up in our food. Their identification is often difficult, or in some cases impossible, making it difficult to assess their safety if exposed. This overview provides an overview of current European regulatory requirements and the latest innovations in NIAS safety assessments. The main conclusion is that an innovative, pragmatic and science-based approach was recently published that can be used to prioritize NIAS based on their exposure and hazards.
research article
Identification of unknown compounds in polyester can coatings that may migrate into food or food simulants
Journal of Chromatography A, Band 1444, 2016, S. 106–113
Cross-linked polyester resins are being marketed as an alternative to epoxy resins as coatings for metal food cans. Due to the diversity of substances used in the manufacture of paints, identifying potential migration of these paints into food is a significant analytical challenge. However, this identification is needed to assess migration from can coatings to food and to assess dietary exposure quantification. Polyester can coatings were extracted with acetonitrile at 40°C for 24 hours, and the extracts were analyzed using various analytical techniques, including GC-MS, HPLC-DAD/MS, HPLC-DAD/CAD, and UHPL C-HRMS. Twenty-nine non-volatile oligomers were tentatively identified using retention time, UV spectroscopy, and accurate mass measurements. The oligomers identified indicated that the food can coating used was a polyester coating mainly based on the monomers isophthalic, terephthalic and nadic acids. To ensure certainty of identification, one of the provisionally identified oligomers was synthesized and analyzed13C and1H NMR and UHPL-C HRMS. NMR and HRMS results confirmed the presence of the compound in the jar extract. Finally, to determine if rapid, direct detection of oligomers was feasible, the coating was analyzed using DART-HRMS. 23 of 29 oligomers in the coating were identified within minutes by direct measurement using DART-HRMS.
research article
Identification of unintentionally added substances in nanofilms for food packaging by gas chromatography-liquid chromatography-orbitrap mass spectrometry
Talanta,Band 172,2017,S.68-77
Controlling chemical migration of novel functionalized food contact materials (FCMs) is a challenge in meeting food safety requirements. Intentionally Added Substances (NIAS) represent a group of chemical substances that are not used but may be introduced or formed during FCM production. This study describes a multi-analytical approach to assess migration of unknown substances from FCM. A case study was performed using a developed polymer consisting of a monolayer film containing polylactic acid (PLA), polylimonene (PL), and zinc oxide nanoparticles (ZnO NPs). The method included an ICP-MS (inductively coupled plasma mass spectrometry) platform to determine the transfer of ZnO NPs used as antimicrobial agents, as well as GC-MS and LC-MS (gas/liquid chromatography coupled to a quadrupole). Orbitrap mass spectrometer) to characterize the chemical structure of NIAS using specific signatures of molecular mass and mass fragmentation. Screening of unknown compounds involved retrospective analysis and data processing using mass spectral libraries and databases of GC and LC data, respectively. This method provided preliminary identification and quantification of seven NIAS, 3 by GC (tripropylene glycol diacrylate, 10-eicosene, and α-tocopheryl acetate) and 4 by LC (N,N -Diethyldodecylamide, N-[(9Z)-9-octadecen-1-yl]acetamide, 1-palmitoylglycerol and glyceryl stearate). This migration study was carried out according to the standard protocol set out in the EU Food Contact Materials Regulation.
research article
Targeted and Untargeted Data-Dependent Experiments for the Characterization of Food Contact Plastics Made of Polycarbonate Using Ultra-Performance Chromatography and Quadrupole Orbitrap Tandem Mass Spectrometry
Journal of Chromatography A, Band 1372, 2014, S. 133–144
Food contact materials are potential sources of chemical food contamination. Therefore, it is critical to characterize the composition of several unknown molecules such as unintentionally added substances (NIAS), residual monomers, degradation products, plastic additives and organic colorants, which may be present. Previous studies on compositional characterization have mainly focused on the detection of additives. To the best of the authors' knowledge, there are no scientific data on the composition of plastic materials in relation to colorants.
In this work, the analytical methods of capillary ultra-high performance liquid chromatography and high-resolution electrospray ionization quadrupole orbitrap mass spectrometry (UHPLC-ESI Q-Orbitrap) were used to characterize polycarbonates for food contact materials. After the polycarbonate samples were completely dissolved and their components extracted, data-dependent experiments for targeted and non-targeted analysis were performed. The presence of common additives such as antioxidants and UV absorbers was confirmed by targeted analysis, while a non-targeted approach combined with the high mass precision of the Orbitrap technology allowed for the first time to identify some polycarbonate degradation products and effectively used organic dyes for food administration Coloring of contacted plastic objects. This study demonstrates the great potential of this technique in the field of material characterization for food safety assessment.
research article
Inadvertently Added Substances (NIAS) in Recycled Plastics
Chemosphere, Volume 251, 2020, Number 126373
Demand for high-quality recycled polymers in the European plastics industry is increasing, possibly due to the EU Plastics Strategy aimed at implementing a circular economy model in the industry. The problem is that there isn't enough recycled plastic on the market. In terms of volume, post-consumer plastic waste can be critical to meeting current and future demand. However, high levels of contamination during the product life cycle limit its use. The first step in changing this must be the identification of undesirable substances in post-consumer plastics and effective risk assessment. The knowledge gained will be the basis for the development of innovative decontamination technologies.
In this study, 134 substances, including volatile and semivolatile compounds, were identified in LDPE and HDPE recovered from municipal waste. Use headspace and solvent extraction followed by GC/MS. For each substance, possible sources were investigated. The main categories are additives, degradation products of polymers and additives, and impurities of external origin. The results showed that recycled LDPE contained a large amount of additives and their degradation products. Some of these may pose security concerns when reused in higher value-added applications. For recycled HDPE, contaminants from the use stage dominate, causing problems such as strong odors. In order to reduce the amount of undesirable substances, it is recommended to limit the types of additives used in plastic production and to choose a separate waste collection system to prevent cross-contamination with organic waste.
research article
Volatile Accidentally Added Substances (NIAS) Found in Recycled Expanded Polystyrene Containers and Their Migration to Food Simulants
Food Packaging and Shelf Life, Volume 20, 2019, Article 100318
Recycled materials such as expanded polystyrene (EPS) are increasingly found in the food market, and recycled PS resin may contain some harmful chemicals. Therefore, the approach of solid-phase microextraction and gas chromatography coupled with mass spectrometry, followed by the application of chemometric tools to the obtained data, can identify markers of new and recovered EPS. A multivariate statistical analysis was developed to characterize the volatile organic compound (VOC) signature in new and recycled EPS containers and to identify potential VOC markers that lead to EPS container discrimination. A total of 99 compounds were identified in new and recycled EPS containers. Among them, 17 compounds that contributed most to the discrimination were selected according to their variable importance in the predicted value (VIP), including o-xylene, acetophenone, ethylbenzene, α-ethylstyrene, 2- Phenylacrolein, propylbenzene, 2-phenyl-1-propene, undecanal, ethyl benzoate, 2-ethyl-1-hexanol, decanal, benzyl formaldehyde, cumene, 2, 4-Diphenyl-1-butene, dodecanal, benzaldehyde and nonanal. To assess the health risks of EPS containers, migration tests were performed on EPS containers in two food simulants (10% ethanol, 3% acetic acid). It should be emphasized that a large amount of styrene was detected. Nevertheless, the analyzed material complies with the current EU Regulation No. 10/2011. The proposed method finds distinguishing marks and provides a reliable tool to distinguish new and recycled EPS containers, which may be an additional tool for quality control of EPS containers.
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