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Preparative HPLC followed by GPC-MS to investigate the potential leachable compounds produced by the degradation of pentaerythritol tetrakis (3-(3,5-di-tert-butyl-4-hydroxyphenyl) propionate)

Applications | 2018 | Agilent TechnologiesInstrumentation
HPLC, LC/MS, GPC/SEC, LC/SQ
Industries
Materials Testing
Manufacturer
Agilent Technologies

Summary

Significance of the Topic


Investigating degradation products of high-performance polymer additives is critical for ensuring material stability and safety. Sterically hindered phenolic antioxidants such as pentaerythritol tetrakis(3-(3,5-di-tert-butyl-4-hydroxyphenyl) propionate) (additive 1010) protect plastics against thermo-oxidative degradation but may generate lower-molecular-weight fragments that migrate into contacting media. Characterizing these non-intentionally added substances supports regulatory compliance and risk assessment of polymer materials.

Study Objectives and Overview


This study demonstrates a combined preparative HPLC and gel permeation chromatography–mass spectrometry (GPC-MS) workflow to isolate and identify high-molecular-weight fragments resulting from additive 1010 degradation. Seven fractions were collected by preparative HPLC, concentrated, and analyzed by GPC-MS to elucidate potential leachable compounds.

Methodology


  • Preparative HPLC fractionation using a C18 reversed-phase column with water/methanol gradient and UV detection at 270 nm to separate additive 1010 and its degradation products into seven discrete fractions.
  • Concentration of collected fractions under vacuum and redissolution in chloroform prior to GPC-MS analysis.
  • GPC separation by molecular size on Resipore columns with chloroform mobile phase, coupled to a single quadrupole mass detector operating in SCAN and SIM modes for fragment identification.

Instrumentation


  • Agilent Infinity II preparative system: 1290 Infinity Binary pump, 1260 Infinity DAD, 1260 Infinity Fraction Collector.
  • Agilent Infinity 1260 system with single quadrupole MS detector.
  • Zorbax SB C18 preparative column, 21.5 × 50 mm, 5 µm.
  • Agilent Resipore GPC columns, 4.6 × 250 mm.

Key Results and Discussion


  • High reproducibility of preparative HPLC confirmed by overlay of repeated injections.
  • Seven fractions obtained and successfully concentrated for downstream GPC-MS.
  • GPC-MS analysis of PS580 standard validated separation of oligomers with degrees of polymerization from 4 to 18, eluting between 16 and 19 min.
  • Analysis of HPLC fractions revealed multiple degradation fragments of additive 1010, including:
    • 1010-I (C56H84O10): loss of one propionate arm;
    • 1010-II (C39H60O8): loss of two arms;
    • 1010-III (C69H100O12): absence of two tert-butyl groups;
    • 1010-IV (C65H92O12): missing two tertiary groups;
    • 1010-V (C52H76O10): loss of one arm and one butyl group.
  • Isotope distribution patterns and SIM extraction facilitated confident structural proposals for each fragment.

Benefits and Practical Applications


  • Efficient isolation and structural characterization of high-molecular-weight, nonvolatile additive degradation products.
  • Supports safety evaluation of migrating compounds in plastic materials, including food-contact applications.
  • Enhances analytical capabilities in polymer formulation, quality control, and regulatory compliance.

Future Trends and Opportunities


  • Extension of the workflow to diverse polymer additives and more complex matrices.
  • Integration with high-resolution mass spectrometry and non-targeted screening strategies for comprehensive profiling of NIAS.
  • Automation and miniaturization of preparative and GPC separation steps to increase throughput.
  • Development of environmentally friendly solvents and sustainable chromatography practices.

Conclusion


The combined preparative HPLC and GPC-MS approach provides a robust, reproducible strategy to isolate and identify high-molecular-weight degradation fragments of sterically hindered phenolic antioxidants. This method addresses challenges in characterizing non-intentionally added substances, thereby facilitating safety assessments and regulatory compliance in polymer applications.

References


  1. D. Brocca, E. Arvin, H. Mosbæk, Identification of organic compounds migrating from polyethylene pipelines into drinking water, Water Research, vol 36, 3675–3680 (2002).
  2. A. Boborodea, G. Cleaver, Gel permeation chromatography – atmospheric pressure chemical ionization – mass spectrometry for oligomer characterization, Int. J. Polym. Anal. Charact., vol 22, no 2, 180–186 (2017).
  3. A. Boborodea, A. Brookes, Gel permeation chromatography – atmospheric pressure chemical ionization – mass spectrometry for characterization of polymer additives, Int. J. Polym. Anal. Charact., vol 22, no 3, 210–214 (2017).
  4. A. Boborodea, S. O’Donohue, Assessing the suitability of a green solvent for gel permeation chromatography – mass spectrometry analysis, Int. J. Polym. Anal. Charact., vol 22, no 4, 305–309 (2017).
  5. A. Boborodea, G. Cleaver, Fast Gel Permeation Chromatography – Mass Spectrometry Method for Polymers and Additives Analysis, Int. J. Polym. Anal. Charact., vol 22, no 6, 490–496 (2017).
  6. L. V. Glushkova et al., Method of extracting pentaerythryl-tetrakis-[3-(3,5-ditert. butyl-4-oxyphenyl)propionate] from the reaction mass, PCT Int. Appl., WO 8905789 A1 (1989).
  7. T. R. Crompton, Additive migration from plastics into foods – A guide for analytical chemists, Smithers Rapra Technology Limited (2007).

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