Method Statement PAHs by GC/MS

@(#) Uncontrolled Document pahgcms.html Version 1.1 Last Revised on 12/09/02




Contents

Introduction

Principle

Performance Characteristics

Range of Application

Limit of Detection

Analytical Quality Control

References

Introduction

The performance of this method is validated in accordance with internationally recognised procedures.

This procedure describes the determination of target polyaromatic hydrocarbons (PAHs) in soils and waters by solvent extraction/concentration followed by analysis of extracts by gas chromatography with mass spectrometeric detection (GC/MS).

Principle

Target PAHs are extracted from an aliquot of the test sample with dichloromethane (in triplicate), after the addition of a mixture of deuterated PAHs to the test sample. The extracts are then combined and reduced in volume to 1ml. The extracts are then analysed by GC/MS in the selected ion recording mode. This is normally performed at unit mass resolution, but if low levels are required analysis is performed at high resolution using a sector mass spectrometer.

Soil samples

0.1 to 10 g aliquots of dried and ground samples are spiked with labelled internal standards then extracted by sonication with three lots of dichloromethane. The three extracts are combined and reduced in volume to circa 1 ml. The PAHs are then analysed by GC/MS.

Water samples

10ml to 1l aliquots of the shaken sample are taken then extracted by liquid/liquid techniques with dichloromethane, after addition of labelled internal standards. The extracts are combined then analysed as for the soils.

Performance Characteristics

Substances Determined

This method is suitable for the analysis of the 'EPA 16' PAHs. These are naphthalene, acenaphthene, acenaphthylene, fluorene, phenanthrene, anthracene, pyrene, fluoranthene, chrysene, benz(a) anthracene, benzo(b)/(k) fluoranthene, benzo(a)pyrene, dibenz(ghi)perylene, indeno(1,2,3,-cd)pyrene and dibenz(a.h) anthracene. Other PAHs may be determined by the method provided suitable standards and validation have been performed.

Range of Application

  • Soils 0.01 to 100 mg/kg (compound dependent)

  • Waters 0.01 to 100 ug/l (compound dependent)

Limit of Detection

  • Soils 0.01-0.1 mg/kg

  • Waters 0.01 ug/l

Analytical Quality Control

Analytical quality control is maintained by a number of measures:

  • Multi-point calibration with authentic standards (with defined minimum performance characteristics)

  • Analysis of control samples within each analytical batch, such as independent standards, matrix spikes or reference materials

  • Analysis of reagent/method blanks within each analytical batch

  • Ongoing quality assured by the use of control charts in conjunction with warning and action limits for the QC sample data

  • Participation in external proficiency testing and interlaboratory schemes such as LGC CONTEST, HSE WASP, CSL FAPAS

References

US EPA Method 8270, Revision C, Semivolatile Organic Compounds by Gas Chromatography – Mass Spectrometery (GC/MS).




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