EPA-NERL: 502.2 (by PID):  VOCs in Water by GC/PID/ELCD

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Volatile Organic Compounds in Water by Purge and Trap Capillary Column Gas Chromatography with Photoionization and Electrolytic Conductivity Detectors in Series
Current Revision
Revision 2.1, 1995
Media
WATER
Instrumentation
Gas Chromatography with Photoionization Detection
Method Subcategory
Organic
Method Source
  EPA-NERL
Citation
  Methods for the Determination of Organic Compounds in Drinking Water - Supplement III (EPA/600/R-95-131)
Brief Method Summary
Inert gas is bubbled through a water sample to purge highly volatile organic compounds with low water solubility. Purged sample compounds are trapped in a tube containing suitable sorbent materials. When purging is complete, the sorbent tube is heated and backflushed with helium to desorb the trapped compounds onto a capillary gas chromatography (GC) column. The concentrations of compounds from the trap are measured using a capillary column GC system equipped with a photoionization detector (PID) and an electrolytic conductivity detector (ELCD) placed in series.
Scope and Application
This method determines purgeable volatile organic compounds (including some disinfection by-products) in finished drinking water, raw source water, or drinking water in any treatment stage.
Applicable Concentration Range
Approximate range is 0.02 - 200 ug/L. Range is analyte and instrument dependent.
Interferences

(A) Contamination of samples with volatiles in the laboratory and impurities in the purge gas and sorbent trap: Use PTFE/Teflon or metal gas lines and plumbing (no out-gassing plastics), and analyze blanks to minimize risk of contamination.

(B) Contamination from sample carryover: Rinsing apparatus with water and purging equipment between analyses can minimize contamination.

(C) Contamination from methylene chloride (MeCl): When determining MeCl (a ubiquitous solvent) wear clothes that have not been exposed to MeCl fumes and use stainless steel or copper carrier gas and plumbing lines (MeCl permeates PTFE) to minimize contamination.

(D) Water collected in the trap: Captured water can be released randomly during analysis. Reconditioning the trap after each use to minimize interference.

Quality Control Requirements

Initial demonstration of laboratory capability followed by regular analyses of laboratory reagent blanks (LRBs), field reagent blanks (FRBs), and laboratory fortified blank (LFB). Initial demonstration of laboratory capability includes the analysis of four to seven replicates of an LFB containing each analyte of concern at a concentration in the range of 0.1-5 ug/L. A method detection limit (MDL) must be determined for each analyte.

Sample Handling

Dechlorinate samples using 3 mg of sodium thiosulfate or 25 mg of ascorbic acid per 40 mL of sample to the sample bottle prior to collection. Additional amounts of sodium thiosulfate or ascorbic acid should be added per each 5 mg/L of residual chlorine.

All samples should be collected in duplicate. Overfill all bottles, making sure to leave no bubbles or headspace. Adjust the pH of all samples to less than 2 at the time of collection, but after dechlorination with two drops of 1:1 HCl for each 40 mL of sample. When sampling for THM analysis only, acidification may be omitted if sodium thiosulfate is used to dechlorinate the sample. If sample foams vigorously after addition of HCl, discard the sample, collect a set of duplicate samples, but do not acidify them. Store samples at 4oC until analysis.

Maximum Holding Time
14 days.
Relative Cost
$201 to $400
Sample Preparation Methods