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Determination of 19 Polycyclic Aromatic Hydrocarbon Compounds in Salmon and Beef

Applications | 2020 | Agilent TechnologiesInstrumentation
GC/MSD, GC/MS/MS, Sample Preparation, GC/QQQ, Consumables
Industries
Food & Agriculture
Manufacturer
Agilent Technologies

Summary

Importance of the Topic


Polycyclic aromatic hydrocarbons (PAHs) are persistent, bioaccumulative, and potentially carcinogenic compounds that can contaminate fatty foods such as fish and meat during processing or environmental exposure. Regulatory bodies, including the U.S. FDA and the European Commission, set strict limits on heavy PAHs in seafood and meat to levels below 1 µg/kg. Reliable analytical methods are essential to monitor PAH residues at low part-per-billion concentrations in complex lipid-rich matrices.

Objectives and Study Overview


This work describes the development and validation of a robust multiresidue method for the determination of 19 PAH compounds in salmon and beef. The protocol integrates solid/liquid extraction (SoLE), Agilent Captiva EMR–Lipid cleanup, and GC/MS/MS analysis. Key goals include achieving high PAH recoveries, low detection limits, efficient removal of lipid co-extractives, and compliance with European Commission performance criteria.

Methodology and Instrumentation


Sample preparation comprises:
  • Two-step SoLE using 20:80 ethyl acetate/acetonitrile with ceramic homogenizers and 10 min shaking per step.
  • Cleanup by gravity elution through a 3 mL Captiva EMR–Lipid cartridge, followed by a supplementary elution with 16:64:20 EtOAc/ACN/water to maximize recovery.
  • Water removal and solvent exchange via back-extraction into isooctane (1:1, v/v) to produce a GC-amenable extract.

Used Instrumentation


  • Agilent 7890B gas chromatograph with electronic pneumatic control (EPC), multimode inlet (MMI), and backflush capability.
  • Agilent 7000D triple quadrupole mass spectrometer operated in dynamic MRM mode.
  • Agilent 7693A autosampler and positive pressure manifold (PPM-48) for cartridge processing.
  • Captiva EMR–Lipid cartridges (3 mL, 300 mg) and associated ceramic homogenizers.

Main Results and Discussion


Validation in salmon and beef matrices showed:
  • Calibration linearity (1–500 ng/g) with R² > 0.99 for all analytes.
  • Mean recoveries between 50 % and 120 % and RSD < 20 % at spiking levels of 1, 10, and 100 ng/g.
  • LOQ established at 1 ng/g for most PAHs; critical heavy PAHs (benzo[a]pyrene, benzo[a]anthracene, benzo[b]fluoranthene, chrysene) are reliably detected at 1 ng/g with S/N > 10.
  • Matrix co-extractive removal of 60 % in salmon and 92 % in beef, significantly reducing lipid interference.

Benefits and Practical Applications


The optimized workflow delivers a streamlined, reproducible approach for routine monitoring of PAHs in high-fat foods. It simplifies cleanup, reduces solvent use, and enables quantitation at regulatory levels without extensive user intervention. Laboratories can adapt this method for quality control, food safety testing, and regulatory compliance.

Future Trends and Potential Applications


Opportunities for further advancement include:
  • Extension to other lipid-rich matrices (dairy, oils, processed foods).
  • Automation and miniaturization of the sample preparation steps.
  • Integration with high-resolution mass spectrometry for non-target screening.
  • Continuous refinement of lower detection limits to meet emerging regulatory standards.

Conclusion


An efficient multiresidue GC/MS/MS method combining SoLE, Captiva EMR–Lipid cleanup, and isooctane back-extraction has been established for reliable determination of 19 PAHs in salmon and beef. The method meets stringent recovery, precision, and sensitivity requirements, offering a powerful tool for food safety laboratories.

References


  1. U.S. Food and Drug Administration, Protocol for Interpretation and Use of Sensory Testing and Analytical Chemistry Results for Re-Opening Oil-Impacted Areas Closed to Seafood Harvesting, 2010.
  2. European Commission Regulation (EC) 836/2011, Official Journal of the European Union, 2011, 215, 9.
  3. Takigami H.; et al. Brominated flame retardants and other polyhalogenated compounds in indoor air and dust from two houses in Japan. Chemosphere 2009, 76, 270–277.
  4. Viegas O.; et al. A comparison of the extraction procedures and quantification methods for the chromatographic determination of polycyclic aromatic hydrocarbons in charcoal grilled meat and fish. Talanta 2012, 88, 677–683.
  5. Stapleton H.M.; et al. Determination of polybrominated diphenyl ethers in environmental reference materials. Anal. Bioanal. Chem. 2007, 387, 2365–2379.
  6. Forsberg N.D.; Wilson G.R.; Anderson K.A. Determination of parent and substituted PAHs in high-fat salmon using modified QuEChERS extraction, dispersive SPE and GC-MS. J. Agric. Food Chem. 2011, 59, 8108–8116.
  7. Sverko E.; et al. Dechlorane plus levels in sediment of the lower Great Lakes. Environ. Sci. Technol. 2008, 42, 361–366.
  8. Saito K.; et al. Development of an accelerated solvent extraction and gel permeation chromatography method for measuring persistent organohalogen compounds in adipose and organ tissue. Chemosphere 2004, 57, 373–381.
  9. Zhao L. Determination of multiclass, multiresidue pesticides in olive oil by Captiva EMR–Lipid cleanup and GC/MS/MS. Agilent Technologies Application Note 5994-0405EN, 2015.
  10. Lucas D.; Zhao L. PAH analysis in salmon with enhanced matrix removal. Agilent Technologies Application Note 5991-6088EN, 2015.
  11. Szelewski M.; Quimby B.D. Optimized PAH analysis using the Agilent self-cleaning ion source and the enhanced PAH analyzer. Agilent Technologies Application Note 5991-3003EN.

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