EPA-OGWDW/TSC: 524.3: Purgeable Organic Compounds in Water by GCMS
- Summary
- Analytes
- Revision
- Data and Sites
Official Method Name
|
Measure of Purgeable Organic Compounds in Water by Capillary Column Gas Chromatography/Mass Spectrometry | ||||
---|---|---|---|---|---|
Current Revision
| Version 1.0, June 2009 | ||||
Media
|
WATER | ||||
Instrumentation
|
Gas Chromatography with Mass Spectrometry Detection | ||||
Method Subcategory
|
Organic | ||||
Method Source
|
EPA-OGWDW/TSC
|
||||
Citation
|
USEPA, 2009, Method 524.3, V. 1: Measurement of Purgeable Organic Compounds in Water by Capillary Column Gas Chromatography/Mass Spectometry, EPA 815-B-09-009. | ||||
Brief Method Summary
|
Headspace-free samples are collected in amber, glass vials with polytetrafluoroethylene (PTFE)-faced septa. Samples are dechlorinated with ascorbic acid and the pH is adjusted with maleic acid. A 5.0-milliliter (mL) aliquot of the sample is transferred to a glass sparging vessel along with appropriate amounts of internal standard and quality control compounds. The method analytes are purged from the water using helium and trapped on a sorbent material. After purging, the trap may be dry purged for a short period to remove water. Additional water management techniques may be applied. The trap is heated and backflushed with helium to transfer the analytes directly into a gas chromatographic inlet. The inlet is operated in the split mode in order to achieve the desired desorb flow rates and further reduce water transmission. Analytes are transferred onto a capillary GC column, which is temperature programmed to optimize the separation of method analytes. Compounds eluting from the GC are directed into a mass spectrometer for detection and quantitation. The method analytes are identified by comparing the acquired mass spectra and retention times to reference spectra and retention times for calibration standards acquired under identical GC/MS conditions. The concentration of each analyte is calculated using the internal standard technique and response curves obtained via procedural calibration (Sect. 3.18). | ||||
Scope and Application
|
This is a gas chromatography/mass spectrometry (GC/MS) method for the determination of purgeable organic compounds in finished drinking waters. Discontinuous scanning modes such as selected ion monitoring (SIM) and selected ion storage (SIS) are permitted for determining selected analytes that are monitored at levels too low for the full scan detection mode. | ||||
Applicable Concentration Range
|
|||||
Interferences
|
Volatile organic compounds (VOCs) present in ambient air, shipping containers, and in the laboratory environment may permeate the PTFE-lined septa of the sample vials or be present at high concentrations in the headspace of the vial. Commercially available purge-and-trap concentrators and autosamplers have complex sample paths that are subject to cross contamination. All laboratory reagents must be routinely demonstrated to be free from interferences under the conditions of the analysis. Matrix interferences are caused by contaminants that are present in the sample. | ||||
Quality Control Requirements
|
At a minimum, collect all samples in duplicate. Duplicate field reagent blanks must accompany each sample set, which is composed of the samples collected from the same general sampling site at approximately the same time. | ||||
Sample Handling
|
Samples must be acidified with maleic and ascorbic acid to ensure a pH of about 2. Samples must be chilled during shipment and must not exceed 10 degrees C during the first 48 hours after collection. | ||||
Maximum Holding Time
|
Samples must be analyzed within 14 days of collection. | ||||
Relative Cost
|
$201 to $400 | ||||
Sample Preparation Methods
|
This method has 76 analytes associated with it.
Analyte | Detection Level |
Bias | Precision | Pct False Positive |
Pct False Negative |
Spiking Level |
---|---|---|---|---|---|---|
1,1,1,2-Tetrachloroethane(630-20-6)
|
0.029 ug/L | N/A | 8.60 RSD | 1.00 ug/L | ||
1,1,1-Trichloroethane(71-55-6)
|
0.026 ug/L | N/A | 10.00 RSD | 1.00 ug/L | ||
1,1,2,2-Tetrachloroethane(79-34-5)
|
0.013 ug/L | N/A | 6.70 RSD | 1.00 ug/L | ||
1,1,2-Trichloroethane(79-00-5)
|
0.048 ug/L | N/A | 7.30 RSD | 1.00 ug/L | ||
1,1-Dichloroethane(75-34-3)
|
0.020 ug/L | N/A | 7.20 RSD | 1.00 ug/L | ||
1,1-Dichloroethene(75-35-4)
|
0.049 ug/L | N/A | 9.00 RSD | 1.00 ug/L | ||
1,1-Dichloropropene(563-58-6)
|
0.082 ug/L | N/A | 8.00 RSD | 1.00 ug/L | ||
1,2,3-Trichlorobenzene(87-61-6)
|
0.020 ug/L | N/A | 6.60 RSD | 1.00 ug/L | ||
1,2,3-Trichloropropane(96-18-4)
|
0.050 ug/L | N/A | 9.90 RSD | 1.00 ug/L | ||
1,2,4-Trichlorobenzene(120-82-1)
|
0.013 ug/L | N/A | 7.20 RSD | 1.00 ug/L | ||
1,2,4-Trimethylbenzene(95-63-6)
|
0.015 ug/L | N/A | 8.10 RSD | 1.00 ug/L | ||
1,2-Dibromoethane(106-93-4)
|
0.018 ug/L | N/A | 7.90 RSD | 1.00 ug/L | ||
1,2-Dichlorobenzene(95-50-1)
|
0.019 ug/L | N/A | 8.30 RSD | 1.00 ug/L | ||
1,2-Dichloroethane(107-06-2)
|
0.025 ug/L | N/A | 7.40 RSD | 1.00 ug/L | ||
1,2-Dichloropropane(78-87-5)
|
0.018 ug/L | N/A | 8.90 RSD | 1.00 ug/L | ||
1,3-Butadiene(106-99-0)
|
0.013 ug/L | N/A | 8.00 RSD | 1.00 ug/L | ||
1,3-Dichlorobenzene(541-73-1)
|
0.012 ug/L | N/A | 6.20 RSD | 1.00 ug/L | ||
1,3-Dichloropropane(142-28-9)
|
0.030 ug/L | N/A | 9.50 RSD | 1.00 ug/L | ||
1,4-Dichlorobenzene(106-46-7)
|
0.015 ug/L | N/A | 7.50 RSD | 1.00 ug/L | ||
Allyl chloride(107-05-1)
|
0.035 ug/L | N/A | 9.80 RSD | 1.00 ug/L | ||
Benzene(71-43-2)
|
0.017 ug/L | N/A | 7.80 RSD | 1.00 ug/L | ||
Bromobenzene(108-86-1)
|
0.020 ug/L | N/A | 9.10 RSD | 1.00 ug/L | ||
Bromochloromethane(74-97-5)
|
0.033 ug/L | N/A | 9.30 RSD | 1.00 ug/L | ||
Bromodichloromethane(75-27-4)
|
0.014 ug/L | N/A | 8.70 RSD | 1.00 ug/L | ||
Bromoform(75-25-2)
|
0.040 ug/L | N/A | 8.10 RSD | 1.00 ug/L | ||
Bromomethane(74-83-9)
|
0.037 ug/L | N/A | 10.00 RSD | 1.00 ug/L | ||
Butane, 2-ethoxy-2-methyl-(919-94-8)
|
0.016 ug/L | N/A | 2.50 RSD | 1.00 ug/L | ||
Carbon disulfide(75-15-0)
|
0.031 ug/L | N/A | 8.90 RSD | 1.00 ug/L | ||
Carbon tetrachloride(56-23-5)
|
0.044 ug/L | N/A | 7.60 RSD | 1.00 ug/L | ||
Chlorobenzene(108-90-7)
|
0.019 ug/L | N/A | 7.20 RSD | 1.00 ug/L | ||
Chlorodifluoromethane(75-45-6)
|
0.022 ug/L | N/A | 9.20 RSD | |||
Chloroform(67-66-3)
|
0.025 ug/L | N/A | 5.30 RSD | 1.00 ug/L | ||
Chloromethane(74-87-3)
|
0.034 ug/L | N/A | 6.70 RSD | 1.00 ug/L | ||
Cumene(98-82-8)
|
0.011 ug/L | N/A | 7.30 RSD | 1.00 ug/L | ||
DBCP(96-12-8)
|
0.063 ug/L | N/A | 8.20 RSD | 1.00 ug/L | ||
Dibromochloromethane(124-48-1)
|
0.027 ug/L | N/A | 7.90 RSD | 1.00 ug/L | ||
Dibromomethane(74-95-3)
|
0.045 ug/L | N/A | 6.90 RSD | 1.00 ug/L | ||
Dichlorodifluoromethane(75-71-8)
|
0.016 ug/L | N/A | 8.50 RSD | 1.00 ug/L | ||
Diethyl ether(60-29-7)
|
0.039 ug/L | N/A | 8.00 RSD | 1.00 ug/L | ||
Diisopropyl ether(108-20-3)
|
0.014 ug/L | N/A | 2.40 RSD | 1.00 ug/L | ||
Ethyl methacrylate(97-63-2)
|
0.030 ug/L | N/A | 7.20 RSD | 1.00 ug/L | ||
Ethylbenzene(100-41-4)
|
0.010 ug/L | N/A | 9.20 RSD (SL) | 1.00 ug/L | ||
Hexachlorobutadiene(87-68-3)
|
0.062 ug/L | N/A | 12.00 RSD | 1.00 ug/L | ||
Hexachloroethane(67-72-1)
|
0.069 ug/L | N/A | 8.60 RSD | 1.00 ug/L | ||
Iodomethane(74-88-4)
|
0.050 ug/L | N/A | 7.50 RSD | 1.00 ug/L | ||
MTBE(1634-04-4)
|
0.020 ug/L | N/A | 6.40 RSD | 1.00 ug/L | ||
Mesitylene(108-67-8)
|
0.015 ug/L | N/A | 9.00 RSD | 1.00 ug/L | ||
Methyl acetate(79-20-9)
|
0.030 ug/L | N/A | 20.00 RSD | 1.00 ug/L | ||
Methylene chloride(75-09-2)
|
0.140 ug/L | N/A | 5.60 RSD | 1.00 ug/L | ||
Naphthalene(91-20-3)
|
0.012 ug/L | N/A | 7.50 RSD | 1.00 ug/L | ||
Pentachloroethane(76-01-7)
|
0.043 ug/L | N/A | 8.40 RSD | 1.00 ug/L | ||
Styrene(100-42-5)
|
0.011 ug/L | N/A | 8.80 RSD | 1.00 ug/L | ||
Tert-Butyl Alcohol(75-65-0)
|
0.046 ug/L | N/A | 4.30 RSD | 1.00 ug/L | ||
Tetrachloroethene(127-18-4)
|
0.036 ug/L | N/A | 8.80 RSD | 1.00 ug/L | ||
Tetrahydrofuran(109-99-9)
|
0.140 ug/L | N/A | 7.40 RSD | 1.00 ug/L | ||
Toluene(108-88-3)
|
0.024 ug/L | N/A | 9.60 RSD | 1.00 ug/L | ||
Trichloroethene(79-01-6)
|
0.035 ug/L | N/A | 7.90 RSD | 1.00 ug/L | ||
Trichlorofluoromethane(75-69-4)
|
0.030 ug/L | N/A | 10.00 RSD | 1.00 ug/L | ||
Vinyl chloride(75-01-4)
|
0.029 ug/L | N/A | 8.10 RSD | 1.00 ug/L | ||
cis-1,2-Dichloroethene(156-59-2)
|
0.042 ug/L | N/A | 8.90 RSD | 1.00 ug/L | ||
cis-1,3-Dichloropropene(10061-01-5)
|
0.026 ug/L | N/A | 6.40 RSD | 1.00 ug/L | ||
m-Xylene(108-38-3)
|
0.020 ug/L | N/A | 9.20 RSD | 1.00 ug/L | ||
n-Butyl chloride(109-69-3)
|
0.020 ug/L | N/A | 7.30 RSD | 1.00 ug/L | ||
n-Butylbenzene(104-51-8)
|
0.045 ug/L | N/A | 11.00 RSD | 1.00 ug/L | ||
n-Propylbenzene(103-65-1)
|
0.008 ug/L | N/A | 9.90 RSD | 1.00 ug/L | ||
o-Chlorotoluene(95-49-8)
|
0.023 ug/L | N/A | 8.50 RSD | 1.00 ug/L | ||
o-Xylene(95-47-6)
|
0.010 ug/L | N/A | 8.30 RSD | 1.00 ug/L | ||
p-Chlorotoluene(106-43-4)
|
0.014 ug/L | N/A | 7.60 RSD | 1.00 ug/L | ||
p-Cymene(99-87-6)
|
0.012 ug/L | N/A | 11.00 RSD | 1.00 ug/L | ||
p-Xylene(106-42-3)
|
0.020 ug/L | N/A | 9.20 RSD | 1.00 ug/L | ||
sec-Butylbenzene(135-98-8)
|
0.012 ug/L | N/A | 10.00 RSD | 1.00 ug/L | ||
tert-Amyl methyl ether(994-05-8)
|
0.017 ug/L | N/A | 1.90 RSD | 1.00 ug/L | ||
tert-Butyl ethyl ether(637-92-3)
|
0.010 ug/L | N/A | 2.00 RSD | 1.00 ug/L | ||
tert-Butylbenzene(98-06-6)
|
0.020 ug/L | N/A | 8.60 RSD | 1.00 ug/L | ||
trans-1,2-Dichloroethene(156-60-5)
|
0.050 ug/L | N/A | 6.80 RSD | 1.00 ug/L | ||
trans-1,3-Dichloropropene(10061-02-6)
|
0.032 ug/L | N/A | 8.40 RSD | 1.00 ug/L |
Precision Descriptor Notes: | |
---|---|
Detection Level Note: | The Detection Limit (DL) is dependent on sample matrix, fortification concentration, and instrument performance. DLs for method analytes fortified into reagent water ranged from 0.0077 to 0.14 µg/L in the full scan mode. These values are presented in Table 6 EPA Document #EPA 815-B-09-009. DLs were also determined for selected analytes in SIM mode. |
Revision | PDF/Link |
---|---|
Version 1.0, June 2009 |
The Water Quality Portal contains
sample results from
sites that use this method.
Download WQP data
Select data:
File format:
Sites where this method was used
Loading Sites ...