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Analysis of PolyChlorinated Biphenyls (PCBs) by GC/MS

Applications | 2011 | Thermo Fisher ScientificInstrumentation
GC/MSD, GC/IT, GC columns, Consumables
Industries
Environmental
Manufacturer
Thermo Fisher Scientific

Summary

Importance of the Topic


Polychlorinated biphenyls (PCBs) are persistent organic pollutants regulated worldwide due to their toxicity, bioaccumulation potential, and environmental persistence. Reliable identification and quantification of PCBs in industrial and municipal wastewater is essential for regulatory compliance and environmental protection. US EPA Method 608 establishes procedures for initial screening by electron capture detection, while GC/MS confirmatory analysis under Method 625 ensures accurate identification of target PCB congeners.

Objectives and Study Overview


  • Evaluate the suitability of the TraceGOLD™ TG-5SilMS capillary column for confirmatory PCB analysis following US EPA Method 608.
  • Demonstrate the chromatographic performance and identification reliability when coupling TRACE™ GC Ultra to an ion trap mass spectrometer.
  • Assess sensitivity, peak shape, and resolution for key PCB congeners across a representative standard mix.

Used Instrumentation


  • Thermo Scientific TRACE™ GC Ultra gas chromatograph with splitless injection (1 µL sample volume, injector at 275 °C).
  • Thermo Scientific TraceGOLD™ TG-5SilMS column (30 m × 0.25 mm × 0.25 µm) with 2 m guard column.
  • Thermo Scientific TriPlus autosampler.
  • Thermo Scientific Ion Trap MS (ITD 230 LT) operated in EI+ segmented scan mode (45–450 amu).
  • Data acquisition and processing via Thermo Scientific Xcalibur software.

Methodology and Analytical Details


A 1 ng/µL standard mixture of seven PCB congeners specified in US EPA Method 608 was analyzed. Samples were injected in splitless mode with helium carrier gas at a constant flow of 1.5 mL/min. The oven program began at 60 °C (5 min hold), ramped at 8 °C/min to 300 °C (10 min hold). The ion trap MS was operated at 70 eV electron energy, source temperature 225 °C, with filament delay of 5 min. Segmented scanning allowed grouping of target ions to enhance signal-to-noise and improve quantitative ion ratio precision.

Main Results and Discussion


Chromatograms of the PCB standard mix showed sharp, symmetrical peaks with baseline separation for all seven congeners. Retention times matched expected values, enabling unambiguous identification. The nonpolar silarylene phase of the TG-5SilMS column minimized interactions with active sites, reducing peak tailing and enhancing resolution. The segmented ion trap approach delivered consistent ion ratios for confirmatory criteria under US EPA Method 625.

Benefits and Practical Applications


  • Regulatory compliance: Meets US EPA confirmatory requirements for PCB monitoring in wastewater.
  • Robust performance: Stable retention times, minimal peak tailing, and high reproducibility.
  • High sensitivity: Detects PCBs at low nanogram levels with reliable ion ratio confirmation.
  • Versatility: Applicable to municipal and industrial discharge analysis, environmental screening, and quality control.

Future Trends and Applications


Emerging directions include coupling advanced GC columns with high-resolution mass spectrometry for even greater selectivity, automated sample preparation and data processing through artificial intelligence algorithms, development of portable GC/MS systems for on-site screening, and expansion into multi-residue methods combining PCBs with other persistent organic pollutants. Green analytical chemistry principles may drive reduced solvent use and miniaturized extraction techniques.

Conclusion


The Thermo Scientific TraceGOLD™ TG-5SilMS column, paired with a TRACE™ GC Ultra and ion trap MS, provides a reliable, high-performance platform for confirmatory analysis of PCBs in accordance with US EPA Method 608. Excellent peak shape, resolution, and sensitivity ensure confident identification and quantification of key congeners in complex wastewater matrices.

Reference


  • US EPA Method 608

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