NOAA NST: 130.30:  Organic contaminants in marine sediments by GC-MS

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Gas chromatography mass spectrometry (GC-MS) analysis for organic contaminates in marine sediments.
Current Revision
March 1998
Media
SOILS/SEDIMENT
Instrumentation
Gas Chromatography with Mass Spectrometry Detection
Method Subcategory
Organic
Method Source
  NOAA NST
Citation
Sampling and Analytical Methods of the National Status and Trends Program Mussel Watch Project: 1993-1996 Update.
NOAA Technical Memorandum NOS ORCA 130. March 1998. Silver Spring, MD. 233pp.
Brief Method Summary
Polycyclic aromatic hydrocarbons (PAH), PCDDs, and PCDFs can be determined at low concentrations by mass spectrometry due to their strong molecular ion response. Therefore, GC/MS in the selected ion monitoring mode provides unambiguous and sensitive detection for these compounds. The availability of labeled surrogates internal standards of many of the analytes makes very accurate determinations of analyte concentrations possible. Quantitation was performed by gas chromatography mass spectrometry (GC/MS) in the selected ion monitoring (SIM) mode. Silica gel/alumina cleanup with activated copper is used to remove interfering materials from the sample prior to analysis.
Scope and Application
The quantitative method described in this document was used to determine polycyclic aromatic hydrocarbons (PAH) and their alkylated homologues in extracts of sediments. This method also provides procedures for the detection and quantitative measurement of polychlorinated dibenzo-p-dioxins (tetra- through octa-chlorinated homologues; PCDDs) and polychlorinated dibenzofurans (tetra- through octa-chlorinated homologues; PCDFs) in sediments at pg/g concentrations.
Applicable Concentration Range
1 - 1000 ng / g
Interferences
Method interferences may be caused by contaminants in solvents, reagents, glassware, and other sample processing hardware, and lead to false positives during instrumental analysis. All materials used in this method are routinely demonstrated to be free from interferences by processing procedural blanks identical to samples (one blank per 20 samples or each batch whichever is more frequent). Matrix interferences result from co-extraction of compounds other than the analytes of interest. Elemental sulfur and naturally occurring lipids can cause interferences in the analysis of sediment extracts.
Quality Control Requirements
The quality assurance / quality control requirements are as follows: Method blank. Laboratory blank spike. Ongoing precision and recovery analyses. Matrix spike. Duplicates. Reference material (NIST SRM 1944) analyses. Labeled compound recovery.
Sample Handling
Collect samples in a glass container and store in the dark at or below -20 deg. C. Store extracts in the dark at 4 deg. C.
Maximum Holding Time
6 months (frozen)
Relative Cost
Greater than $400
Sample Preparation Methods
NOAA TM #130