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Analysis of Volatile Organic Compounds (VOC) in Soil (1)

Aplikace |  | ShimadzuInstrumentace
GC/MSD, HeadSpace, Purge and Trap, GC/SQ
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Životní prostředí
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Shimadzu

Souhrn

Significance of the Topic


Volatile organic compounds (VOCs) in soil pose risks to ecosystems and human health due to their toxicity and mobility. Reliable detection and quantification are essential for regulatory compliance, environmental monitoring, and remediation efforts.

Objectives and Study Overview


This study outlines the application of two GC/MS‐based techniques—static headspace and purge‐and‐trap—for analyzing VOCs in soil. It follows recent amendments to Japanese tap water, wastewater and soil pollution standards, aiming to demonstrate method performance under real‐world regulatory requirements.

Methodology and Instrumentation


Sample Preparation:
  • Remove gravel and wood fragments larger than 5 mm from collected soil.
  • Mix 50 g of soil with 500 mL of VOC‐free purified water in a sealed 500 mL flask equipped with a stir bar.
  • Stir at 20 °C for 4 hours, let settle 10–30 minutes, then filter through a 0.45 µm membrane to obtain the test solution.

Analytical Techniques and Conditions:
  • Static Headspace GC/MS
    – Instrument: Shimadzu GCMS-QP5050A with DB-624 column (60 m×0.32 mm I.D., 1.8 µm df).
    – Carrier gas: He at 120 kPa. Temperature program: 40 °C (2 min) to 200 °C at 10 °C/min (2 min).
    – Headspace: 10 mL sample + 3 g NaCl, equilibrated at 60 °C for 30 min; injection port at 150 °C, transfer line at 120 °C.
  • Purge-and-Trap GC/MS
    – Purge system: Tekmar-Dohmann LSC3000 with Tenax-silica gel tube (G-2).
    – Purge: 5 mL sample, 5 min purge (20 °C), dry purge 2 min at 30 mL/min.
    – Thermal desorption: 200 °C for 3 min; trap bake at 220 °C for 2 min; transfer line at 150 °C.
    – GC/MS: Shimadzu GCMS-QP5050A, same column; He 120 kPa; ramp from 40 °C to 200 °C with multiple rates.

Main Results and Discussion


Both methods successfully separated and detected 23 target VOCs including chlorinated hydrocarbons, aromatics and halogenated ethenes.
  • Headspace GC/MS delivered good reproducibility, minimal carry-over and detection limits in the low microgram-per-liter range, as shown by the SIM chromatogram for a 1 µg/L spike.
  • Purge-and-trap GC/MS achieved 10–100× greater sensitivity, enabling trace-level quantification with clearer peak shapes in the SIM chromatogram.

Benefits and Practical Applications


The static headspace method offers ease of use, automation capability and robustness, making it suitable for routine monitoring. The purge-and-trap approach provides superior sensitivity for regulatory compliance in heavily contaminated sites or low-level monitoring scenarios.

Future Trends and Opportunities


Advances may include automated sample preparation workflows, miniaturized purge-trap systems, coupling with high-resolution mass spectrometry for comprehensive screening, and development of field-deployable units for in situ soil monitoring.

Conclusion


Comparative evaluation confirms that static headspace GC/MS delivers reproducible, user-friendly VOC analysis at regulatory levels, while purge-and-trap GC/MS extends detection limits by up to two orders of magnitude, supporting detailed environmental assessments.

References


  • Japan Water Works Association. Drinking Water Test Method & Explanation.
  • Environmental Science Research Group. Environmental Water Analysis Manual.
  • Environmental Science Research Group. New Wastewater Standards and Other Analysis Methods.
  • Central Environment Think Tank. Additional Items for Environment Standard Related to Soil Pollution, January 14, 1994.

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