NOAA NST: 130.11: Organic contaminants in marine animal tissues by GC-ECD
Summary
Analytes
Revision
Data and Sites
Official Method Name
Gas chromatography electron capture detector (GC-ECD) analysis for organic contaminates in marine animal tissues.
Current Revision
March 1998
Media
ANIMAL TISSUE
Instrumentation
Gas Chromatography with Electron Capture Detection
Method Subcategory
Organic
Method Source
NOAA NST
Contact Information:
National Oceanic and Atmospheric Administration (NOAA)
National Status and Trends Program (NS&T)
SSMC-4, N/SCI-1
1305 East West Highway
Silver Spring, MD 20910
Tel. 301-713-3028
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
Chlorinated hydrocarbons are quantitatively determined by gas chromatography with an electron capture detector (ECD). The ECD is very sensitive and allows for detection of the chlorinated hydrocarbons at trace concentrations (ppb) in marine animal tissue. Silica gel/alumina cleanup with activated copper was used to remove interfering materials from the sample prior to analysis.
Scope and Application
This method quantitatively determines chlorinated pesticides and PCBs in animal tissue using GC/ECD.
Applicable Concentration Range
5 to 200 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 tissue extracts.
Quality Control Requirements
The quality assurance / quality control requirements were as follows:
Initial calibration and continuing calibration checks.
Method blank analysis.
Surrogate compound analysis.
Matrix spike analysis.
Reference sample analysis.
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.
Precision and accuracy data were obtained from NOAA's NS&T interlaboratory validation QA program. NOAA Technical memorandum NOS ORCA 138 "National Status and Trends Program for Marine Environmental Quality, NIST/NOAA NS&T Intercomparison Exercise Program for Organic Contaminants in the Marine Envoronment Description and Results of 1998 Organic Intercomparison Exercises".
Detection Level Note:
Federal Register (1984), Vol. 49, No. 209: 198-199.
Revision
PDF/Link
March 1998
The Water Quality Portal contains
sample results from
sites that use this method.