EPA-NERL: 524.2: VOCs in Water Using GCMS
- Summary
- Analytes
- Revision
- Data and Sites
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Official Method Name
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Measurement of Purgeable Organic Compounds in Water by Capillary Column Gas Chromatography/Mass Spectrometry | ||||
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Current Revision
| Revision 4.1, 1995 | ||||
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Media
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WATER | ||||
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Instrumentation
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Gas Chromatography with Mass Spectrometry Detection | ||||
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Method Subcategory
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Organic | ||||
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Method Source
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EPA-NERL
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Citation
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EPA Method Guidance CD-ROM (includes MCAWW Methods, and most current EPA Methods)
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Brief Method Summary
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Inert gas is bubbled through a water sample to purge volatile organic compounds with low water solubility. Purged 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 into a capillary gas chromatography (GC) column. The concentrations of compounds from the trap are measured using a capillary column GC system equipped with a mass spectrometer (MS). | ||||
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Scope and Application
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This method determines purgeable volatile organic compounds (including some disinfection byproducts) in surface water, ground water, and drinking water in any stage of treatment. | ||||
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Applicable Concentration Range
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Approximate range is 0.02 - 200 ug/L for wide-bore thick-film capillary columns and 0.02 - 20 ug/L for narrow-bore thick-film capillary columns. Range is analyte and instrument dependent. | ||||
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Interferences
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(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) Contamination of methanol: Ketones, methylene chloride, and other organic solvents often contaminate even high purity methanol. |
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Quality Control Requirements
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Initial demonstration of laboratory capability followed by regular analyses of laboratory reagent blanks (LRBs), field reagent blanks (FRBs), and laboratory fortified blanks (LFBs). 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 2 - 5 ug/L depending upon the calibration range of the instrumentation. Additional QC procedures are recommended. A method detection limit (MDL) must be determined for each analyte. |
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Sample Handling
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Dechlorinate samples using 25 mg of ascorbic acid per 40 mL of sample added to the sample bottle prior to collection. Additional amounts of ascorbic acid should be added per each 5 mg/L of residual chlorine. Sodium thiosulfate, at 3 mg per 40 mL of each water sample should be added for analytes such as vinyl chloride that are gases at room temperature or if analytes in Table 7 are not to be determined. 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 less than 4oC until analysis. |
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Maximum Holding Time
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14 days. | ||||
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Relative Cost
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$201 to $400 | ||||
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Sample Preparation Methods
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Dechlorination, pH adjustment. |
| Analyte | Detection Level |
Bias | Precision | Pct False Positive |
Pct False Negative |
Spiking Level |
|---|---|---|---|---|---|---|
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1,1,1,2-Tetrachloroethane(630-20-6)
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0.040 ug/L | 100% Rec (SL) | 4.70 % RSD (SL) | 0.10 ug/L | ||
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1,1,1-Trichloroethane(71-55-6)
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0.040 ug/L | 100% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
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1,1,2,2-Tetrachloroethane(79-34-5)
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0.200 ug/L | 100% Rec (SL) | 12.00 % RSD (SL) | 0.50 ug/L | ||
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1,1,2-Trichloroethane(79-00-5)
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0.030 ug/L | 98% Rec (SL) | 4.90 % RSD (SL) | 0.10 ug/L | ||
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1,1-Dichloroacetone(513-88-2)
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1.000 ug/L | 84% Rec (SL) | 7.70 % RSD (SL) | 5.00 ug/L | ||
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1,1-Dichloroethane(75-34-3)
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0.030 ug/L | 98% Rec (SL) | 6.20 % RSD (SL) | 0.10 ug/L | ||
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1,1-Dichloroethene(75-35-4)
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0.050 ug/L | 95% Rec (SL) | 9.00 % RSD (SL) | 0.10 ug/L | ||
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1,2,3-Trichlorobenzene(87-61-6)
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0.040 ug/L | 98% Rec (SL) | 8.90 % RSD (SL) | 0.10 ug/L | ||
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1,2,3-Trichloropropane(96-18-4)
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0.030 ug/L | 96% Rec (SL) | 6.50 % RSD (SL) | 0.10 ug/L | ||
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1,2,4-Trichlorobenzene(120-82-1)
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0.200 ug/L | 91% Rec (SL) | 16.00 % RSD (SL) | 0.10 ug/L | ||
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1,2,4-Triethylbenzene(877-44-1)
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0.040 ug/L | 96% Rec (SL) | 6.50 % RSD (SL) | 0.10 ug/L | ||
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1,2-Dibromoethane(106-93-4)
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0.020 ug/L | 97% Rec (SL) | 5.60 % RSD (SL) | 0.10 ug/L | ||
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1,2-Dichlorobenzene(95-50-1)
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0.050 ug/L | 97% Rec (SL) | 3.50 % RSD (SL) | 0.10 ug/L | ||
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1,2-Dichloroethane(107-06-2)
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0.020 ug/L | 100% Rec (SL) | 6.30 % RSD (SL) | 0.10 ug/L | ||
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1,2-Dichloropropane(78-87-5)
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0.020 ug/L | 96% Rec (SL) | 6.00 % RSD (SL) | 0.10 ug/L | ||
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1,2-Dichloropropene(563-54-2)
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0.020 ug/L | 98% Rec (SL) | 7.40 % RSD (SL) | 0.10 ug/L | ||
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1,3-Dichlorobenzene(541-73-1)
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0.050 ug/L | 99% Rec (SL) | 6.00 % RSD (SL) | 0.10 ug/L | ||
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1,3-Dichloropropane(142-28-9)
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0.040 ug/L | 99% Rec (SL) | 5.80 % RSD (SL) | 0.10 ug/L | ||
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1,4-Dichlorobenzene(106-46-7)
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0.040 ug/L | 93% Rec (SL) | 5.70 % RSD (SL) | 0.01 ug/L | ||
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2-Butyl-2-methyl-1,3-dioxane(25683-00-5)
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0.390 ug/L | 110% Rec (SL) | 12.00 % RSD (SL) | 1.00 ug/L | ||
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2-Hexanone(591-78-6)
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0.390 ug/L | 110% Rec (SL) | 12.00 % RSD (SL) | 1.00 ug/L | ||
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4-Methyl-2-pentanone(108-10-1)
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0.170 ug/L | 140% Rec (SL) | 9.70 % RSD (SL) | 0.40 ug/L | ||
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Acetone(67-64-1)
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0.280 ug/L | 160% Rec (SL) | 5.70 % RSD (SL) | 1.00 ug/L | ||
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Acrylonitrile(107-13-1)
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0.220 ug/L | 81% Rec (SL) | 8.70 % RSD (SL) | 1.00 ug/L | ||
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Allyl chloride(107-05-1)
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0.130 ug/L | 90% Rec (SL) | 4.70 % RSD (SL) | 1.00 ug/L | ||
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Benzene(71-43-2)
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0.030 ug/L | 99% Rec (SL) | 6.20 % RSD (SL) | 0.10 ug/L | ||
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Bromobenzene(108-86-1)
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0.110 ug/L | 97% Rec (SL) | 7.40 % RSD (SL) | 0.50 ug/L | ||
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Bromochloromethane(74-97-5)
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0.070 ug/L | 97% Rec (SL) | 5.80 % RSD (SL) | 0.50 ug/L | ||
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Bromodichloromethane(75-27-4)
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0.030 ug/L | 100% Rec (SL) | 4.60 % RSD (SL) | 0.10 ug/L | ||
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Bromoform(75-25-2)
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0.200 ug/L | 99% Rec (SL) | 5.40 % RSD (SL) | 0.10 ug/L | ||
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Bromomethane(74-83-9)
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0.060 ug/L | 99% Rec (SL) | 7.10 % RSD (SL) | 0.10 ug/L | ||
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Carbon disulfide(75-15-0)
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0.093 ug/L | 95% Rec (SL) | 15.00 % RSD (SL) | 0.20 ug/L | ||
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Carbon tetrachloride(56-23-5)
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0.080 ug/L | 92% Rec (SL) | 6.80 % RSD (SL) | 0.10 ug/L | ||
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Chloroacetonitrile(107-14-2)
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0.120 ug/L | 83% Rec (SL) | 4.70 % RSD (SL) | 1.00 ug/L | ||
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Chlorobenzene(108-90-7)
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0.030 ug/L | 91% Rec (SL) | 5.80 % RSD (SL) | 0.10 ug/L | ||
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Chloroethane(75-00-3)
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0.020 ug/L | 100% Rec (SL) | 5.80 % RSD (SL) | 0.10 ug/L | ||
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Chloroform(67-66-3)
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0.020 ug/L | 95% Rec (SL) | 3.20 % RSD (SL) | 0.10 ug/L | ||
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Chloromethane(74-87-3)
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0.050 ug/L | 99% Rec (SL) | 4.70 % RSD (SL) | 0.10 ug/L | ||
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Cumene(98-82-8)
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0.100 ug/L | 98% Rec (SL) | 6.40 % RSD (SL) | 0.50 ug/L | ||
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Cyanogen chloride (CN)Cl(506-77-4)
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0.300 ug/L | 92% Rec (SL) | 10.60 % RSD (SL) | |||
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DBCP(96-12-8)
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0.050 ug/L | 92% Rec (SL) | 10.00 % RSD (SL) | 0.10 ug/L | ||
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Dibromochloromethane(124-48-1)
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0.070 ug/L | 99% Rec (SL) | 5.60 % RSD (SL) | 0.10 ug/L | ||
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Dibromomethane(74-95-3)
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0.030 ug/L | 93% Rec (SL) | 6.90 % RSD (SL) | 0.10 ug/L | ||
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Dichlorodifluoromethane(75-71-8)
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0.110 ug/L | 99% Rec (SL) | 8.80 % RSD (SL) | 0.10 ug/L | ||
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Diethyl ether(60-29-7)
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0.280 ug/L | 92% Rec (SL) | 9.50 % RSD (SL) | 1.00 ug/L | ||
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Ethyl cyanide(107-12-0)
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0.140 ug/L | 87% Rec (SL) | 5.30 % RSD (SL) | 1.00 ug/L | ||
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Ethyl methacrylate(97-63-2)
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0.028 ug/L | 115% Rec (SL) | 3.90 % RSD (SL) | 0.20 ug/L | ||
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Ethylbenzene(100-41-4)
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0.030 ug/L | 99% Rec (SL) | 5.20 % RSD (SL) | 0.10 ug/L | ||
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Hexachlorobutadiene(87-68-3)
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0.040 ug/L | 100% Rec (SL) | 6.70 % RSD (SL) | 0.10 ug/L | ||
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Hexachloroethane(67-72-1)
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0.057 ug/L | 90% Rec (SL) | 10.00 % RSD (SL) | 0.20 ug/L | ||
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Iodomethane(74-88-4)
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0.019 ug/L | 95% Rec (SL) | 3.10 % RSD (SL) | 0.20 ug/L | ||
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MTBE(1634-04-4)
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0.090 ug/L | 130% Rec (SL) | 5.60 % RSD (SL) | 0.40 ug/L | ||
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Mesitylene(108-67-8)
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0.020 ug/L | 99% Rec (SL) | 4.20 % RSD (SL) | 0.10 ug/L | ||
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Methacrylonitrile(126-98-7)
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0.120 ug/L | 92% Rec (SL) | 4.20 % RSD (SL) | 1.00 ug/L | ||
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Methyl acrylate(96-33-3)
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0.450 ug/L | 120% Rec (SL) | 12.00 % RSD (SL) | 1.00 ug/L | ||
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Methyl ethyl ketone(78-93-3)
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0.480 ug/L | 135% Rec (SL) | 5.60 % RSD (SL) | 2.00 ug/L | ||
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Methyl methacrylate(80-62-6)
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0.430 ug/L | 100% Rec (SL) | 13.00 % RSD (SL) | 1.00 ug/L | ||
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Methylene chloride(75-09-2)
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0.090 ug/L | 97% Rec (SL) | 13.00 % RSD (SL) | 0.50 ug/L | ||
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Naphthalene(91-20-3)
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0.040 ug/L | 98% Rec (SL) | 7.20 % RSD (SL) | 0.10 ug/L | ||
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Nitrobenzene(98-95-3)
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1.200 ug/L | 105% Rec (SL) | 18.00 % RSD (SL) | 2.00 ug/L | ||
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Organics, semivolatile(E-12884)
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N/A | N/A | N/A | |||
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Pentachloroethane(76-01-7)
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0.140 ug/L | 115% Rec (SL) | 20.00 % RSD (SL) | 0.20 ug/L | ||
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Styrene(100-42-5)
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0.060 ug/L | 96% Rec (SL) | 19.00 % RSD (SL) | 0.10 ug/L | ||
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TTHM(N-55743)
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N/A | N/A | N/A | |||
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Tetrachloroethene(127-18-4)
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0.050 ug/L | 96% Rec (SL) | 5.00 % RSD (SL) | 0.10 ug/L | ||
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Tetrahydrofuran(109-99-9)
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1.600 ug/L | 78% Rec (SL) | 13.00 % RSD (SL) | 5.00 ug/L | ||
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Toluene(108-88-3)
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0.080 ug/L | 100% Rec (SL) | 5.90 % RSD (SL) | 0.10 ug/L | ||
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Total xylenes(1330-20-7)
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N/A | N/A | N/A | |||
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Trichloroethene(79-01-6)
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0.020 ug/L | 96% Rec (SL) | 2.00 % RSD (SL) | 0.10 ug/L | ||
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Trichlorofluoromethane(75-69-4)
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0.070 ug/L | 97% Rec (SL) | 4.60 % RSD (SL) | 0.10 ug/L | ||
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Vinyl chloride(75-01-4)
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0.040 ug/L | 96% Rec (SL) | 0.20 % RSD (SL) | 0.10 ug/L | ||
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Volatile organic compounds(E-12419)
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N/A | N/A | N/A | |||
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cis-1,2-Dichloroethene(156-59-2)
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0.060 ug/L | 100% Rec (SL) | 3.70 % RSD (SL) | 0.10 ug/L | ||
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cis-1,3-Dichloropropene(10061-01-5)
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0.020 ug/L | 100% Rec (SL) | 3.10 % RSD (SL) | 0.20 ug/L | ||
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m-Xylene(108-38-3)
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0.030 ug/L | 94% Rec (SL) | 4.60 % RSD (SL) | 0.10 ug/L | ||
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n-Butyl chloride(109-69-3)
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0.180 ug/L | 87% Rec (SL) | 6.60 % RSD (SL) | 1.00 ug/L | ||
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n-Butylbenzene(104-51-8)
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0.030 ug/L | 94% Rec (SL) | 6.00 % RSD (SL) | 0.50 ug/L | ||
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n-Propylbenzene(103-65-1)
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0.060 ug/L | 99% Rec (SL) | 6.60 % RSD (SL) | 0.10 ug/L | ||
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o-Chlorotoluene(95-49-8)
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0.050 ug/L | 99% Rec (SL) | 4.60 % RSD (SL) | 0.10 ug/L | ||
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o-Xylene(95-47-6)
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0.060 ug/L | 94% Rec (SL) | 7.50 % RSD (SL) | 0.10 ug/L | ||
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p-Chlorotoluene(106-43-4)
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0.050 ug/L | 96% Rec (SL) | 7.00 % RSD (SL) | 0.10 ug/L | ||
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p-Cymene(99-87-6)
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0.260 ug/L | 87% Rec (SL) | 13.00 % RSD (SL) | 0.50 ug/L | ||
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p-Xylene(106-42-3)
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0.060 ug/L | 97% Rec (SL) | 6.10 % RSD (SL) | 0.10 ug/L | ||
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sec-Butylbenzene(135-98-8)
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0.120 ug/L | 90% Rec (SL) | 7.10 % RSD (SL) | 0.50 ug/L | ||
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sec-Dichloropropane(594-20-7)
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0.050 ug/L | 99% Rec (SL) | 4.90 % RSD (SL) | 0.10 ug/L | ||
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tert-Butylbenzene(98-06-6)
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0.330 ug/L | 90% Rec (SL) | 2.50 % RSD (SL) | 0.50 ug/L | ||
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trans-1,2-Dichloroethene(156-60-5)
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0.030 ug/L | 98% Rec (SL) | 7.20 % RSD (SL) | 0.10 ug/L | ||
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trans-1,3-Dichloropropene(10061-02-6)
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0.048 ug/L | 110% Rec (SL) | 14.00 % RSD (SL) | 0.10 ug/L | ||
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trans-1,4-Dichloro-2-butene(110-57-6)
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0.360 ug/L | 130% Rec (SL) | 8.70 % RSD (SL) | 1.00 ug/L |
| Precision Descriptor Notes: | Precision and accuracy values were determined using 7 replicate analyses of fortified reagent water. Two instrument configurations were used. One configuration used cryogenic interface (cryogenic trapping), a quadrapole mass spectrometer, and a narrow capillary bore column (see Table 3 of the Method). The other configuration used an ion trap mass spectrometer with a wide-bore capillary column (see Table 7 of the Method). Consult the method to determine how the data for specific analytes were generated and for additional information. NOTE: Total trihalomethanes (TTHMs) and total xylenes are regulatory parameter that represents the sum of compounds. See specific compounds for information on method performance, and see regulatory data for more information. |
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| Detection Level Note: | MDLs were determined using the standard deviation of replicate analyses of an analyte-fortified reagent water sample multiplied by the t-value for (# of samples - 1) degrees of freedom at the 99% confidence level. Detailed instructions for how MDLs are determined are found at 40 CFR part 136, Appendix B. |
| Revision | PDF/Link |
|---|---|
| Revision 4.1, 1995 |



