EPA-OGWDW/TSC: 551.1: Chlorinated Compounds in Water Using GC-ECD
- Summary
- Analytes
- Revision
- Data and Sites
Official Method Name
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Determination of Chlorinated Disinfection Byproducts, Chlorinated Solvents, and Halogenated Pesticides/Herbicides in Drinking Water by Liquid/Liquid Extraction and Gas Chromatography with Electron Capture Detection | ||||
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Current Revision
| Revision 1.0, 1995 | ||||
Media
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WATER | ||||
Instrumentation
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Gas Chromatography with Electron Capture Detection | ||||
Method Subcategory
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Organic | ||||
Method Source
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EPA-OGWDW/TSC
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Citation
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Methods for the Determination of Organic Compounds in Drinking Water - Supplement III (EPA/600/R-95-131)
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Brief Method Summary
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A 50-mL sample is extracted with 3-mL of MTBE or 5-mL of pentane. The concentrations of compounds in the extract are measured using a fused silica capillary column gas chromatography (GC) system equipped a linearized electron capture detector (ECD). | ||||
Scope and Application
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This method determines certain chlorinated or halogenated compounds (disinfection byproducts, pesticides, herbicides, and solvents) in finished drinking water, drinking water during intermediate stages of treatment, and raw source water. | ||||
Applicable Concentration Range
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Ranges differ for each analyte. | ||||
Interferences
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(A) Glassware contamination: Thoroughly clean glassware, including baking or solvent rinse. (B) Solvent contamination: Use high purity solvents, and test solvents to prevent contamination: Contamination of MTBE and pentane with chlorinated solvents (common occurrence) can be reduced by double distillation. (C) Extracted interferences: Interference from extracted non-target compounds, with retention times similar to target compounds, can be reduced using confirmation analysis. (D) Endrin degradation: The splitless injector may cause endrin degradation. Endrin can break down by reacting with the active sites on the port sleeve. (E) Phthalate interference: An unknown interference (probably phthalates) appears in retention windows of metribuzin, alachlor, cyanazine, and heptachlor. Seal containers and avoid sample contact with plastics. |
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Quality Control Requirements
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Laboratory performance check standard, initial demonstration of laboratory capability, method detection limit (MDL) determination, analysis of laboratory reagent blanks (LRBs), continuing calibration check standard, laboratory fortified sample matrices, field duplicates, and monitoring surrogate and/or internal standard peak response in each sample and blank. Additional QC practices may be added. | ||||
Sample Handling
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Two sets of 60-mL vials must be prepared for sampling: one set for all target analytes except chloral hydrate with 100 mg/L of ammonium chloride as a dechlorinating agent and one set for the analysis of chloral hydrate using 100 mg/L of sodium sulfite as the dechlorinating agent. Ammonium chloride must also be used as the dechlorinating agent if samples are to be analyzed for haloacetonitriles, 1,1-dichloro-2-propanone, 1,1,1-trichloro-2-propanone, and chloropicrin. All samples should be collected in duplicate. Overfill all bottles, making sure to leave no bubbles or headspace. Store samples at 4oC until analysis. |
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Maximum Holding Time
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14 days; extracts within 14 days. | ||||
Relative Cost
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$201 to $400 | ||||
Sample Preparation Methods
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Analyte | Detection Level |
Bias | Precision | Pct False Positive |
Pct False Negative |
Spiking Level |
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1,1,1-Trichloro-2-propanone(918-00-3)
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0.010 ug/L | 106% Rec (SL) | 0.81 % RSD (SL) | 5.00 ug/L | ||
1,1,1-Trichloroethane(71-55-6)
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0.005 ug/L | 130% Rec (SL) | 12.35 % RSD (SL) | 0.01 ug/L | ||
1,1,2-Trichloroethane(79-00-5)
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0.010 ug/L | 89% Rec (SL) | 3.27 % RSD (SL) | 0.14 ug/L | ||
1,1-Dichloroacetone(513-88-2)
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0.002 ug/L | 110% Rec (SL) | 6.22 % RSD (SL) | 0.01 ug/L | ||
1,2,3-Trichloropropane(96-18-4)
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0.008 ug/L | 88% Rec (SL) | 1.95 % RSD (SL) | 0.16 ug/L | ||
1,2-Dibromoethane(106-93-4)
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0.008 ug/L | 200% Rec (SL) | 12.54 % RSD (SL) | 0.01 ug/L | ||
Alachlor(15972-60-8)
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0.025 ug/L | 117% Rec (SL) | 2.13 % RSD (SL) | 0.33 ug/L | ||
Atrazine(1912-24-9)
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0.082 ug/L | 121% Rec (SL) | 3.56 % RSD (SL) | 0.63 ug/L | ||
Bromacil(314-40-9)
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0.030 ug/L | 105% Rec (SL) | 10.05 % RSD (SL) | 0.09 ug/L | ||
Bromochloroacetonitrile(83463-62-1)
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0.002 ug/L | 110% Rec (SL) | 5.42 % RSD (SL) | 0.01 ug/L | ||
Bromodichloromethane(75-27-4)
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0.003 ug/L | 120% Rec (SL) | 7.50 % RSD (SL) | 0.01 ug/L | ||
Bromoform(75-25-2)
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0.004 ug/L | 180% Rec (SL) | 8.12 % RSD (SL) | 0.01 ug/L | ||
Carbon tetrachloride(56-23-5)
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0.002 ug/L | 110% Rec (SL) | 6.32 % RSD (SL) | 0.01 ug/L | ||
Chloral hydrate(302-17-0)
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0.005 ug/L | 116% Rec (SL) | 5.61 % RSD (SL) | 0.03 ug/L | ||
Chloroform(67-66-3)
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0.050 ug/L | 102% Rec (SL) | 1.30 % RSD (SL) | 5.00 ug/L | ||
Cyanazine(21725-46-2)
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0.316 ug/L | 134% Rec (SL) | 13.93 % RSD (SL) | 0.57 ug/L | ||
DBCP(96-12-8)
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0.009 ug/L | 200% Rec (SL) | 15.50 % RSD (SL) | 0.01 ug/L | ||
Dibromoacetonitrile(3252-43-5)
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0.006 ug/L | 160% Rec (SL) | 12.78 % RSD (SL) | 0.01 ug/L | ||
Dibromochloromethane(124-48-1)
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0.001 ug/L | 110% Rec (SL) | 4.55 % RSD (SL) | 0.01 ug/L | ||
Dichloroacetonitrile(3018-12-0)
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0.001 ug/L | 90% Rec (SL) | 4.28 % RSD (SL) | 0.01 ug/L | ||
Endrin(72-20-8)
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0.002 ug/L | 144% Rec (SL) | 2.57 % RSD (SL) | 0.02 ug/L | ||
Endrin aldehyde(7421-93-4)
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0.002 ug/L | 105% Rec (SL) | 2.25 % RSD (SL) | 0.02 ug/L | ||
Endrin ketone(53494-70-5)
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0.002 ug/L | 100% Rec (SL) | 5.14 % RSD (SL) | 0.02 ug/L | ||
Heptachlor(76-44-8)
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0.081 ug/L | 112% Rec (SL) | 2.84 % RSD (SL) | 0.31 ug/L | ||
Heptachlor epoxide(1024-57-3)
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0.002 ug/L | 114% Rec (SL) | 1.64 % RSD (SL) | 0.04 ug/L | ||
Herbicides(E-12839)
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N/A | N/A | N/A | |||
Hexachlorobenzene(118-74-1)
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0.001 ug/L | 100% Rec (SL) | 5.44 % RSD (SL) | 0.01 ug/L | ||
Hexachlorocyclopentadiene(77-47-4)
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0.018 ug/L | 100% Rec (SL) | 31.81 % RSD (SL) | 0.02 ug/L | ||
Lindane(58-89-9)
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0.004 ug/L | 167% Rec (SL) | 9.90 % RSD (SL) | 0.01 ug/L | ||
Methoxychlor(72-43-5)
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0.008 ug/L | 90% Rec (SL) | 4.85 % RSD (SL) | 0.06 ug/L | ||
Metolachlor(51218-45-2)
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0.024 ug/L | 116% Rec (SL) | 3.20 % RSD (SL) | 0.22 ug/L | ||
Metribuzin(21087-64-9)
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0.037 ug/L | 161% Rec (SL) | 12.45 % RSD (SL) | 0.06 ug/L | ||
Organics, semivolatile(E-12884)
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N/A | N/A | N/A | |||
Organochlorine pesticides(E-12851)
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N/A | N/A | N/A | |||
Simazine(122-34-9)
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0.142 ug/L | 127% Rec (SL) | 5.95 % RSD (SL) | 0.63 ug/L | ||
TTHM(N-55743)
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N/A | N/A | N/A | |||
Tetrachloroethene(127-18-4)
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0.002 ug/L | 120% Rec (SL) | 5.04 % RSD (SL) | 0.01 ug/L | ||
Trichloroacetonitrile(545-06-2)
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0.002 ug/L | 100% Rec (SL) | 5.31 % RSD (SL) | 0.01 ug/L | ||
Trichloroethene(79-01-6)
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0.002 ug/L | 80% Rec (SL) | 8.68 % RSD (SL) | 0.01 ug/L | ||
Trifluralin(1582-09-8)
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0.003 ug/L | 118% Rec (SL) | 3.89 % RSD (SL) | 0.02 ug/L | ||
Volatile organic compounds(E-12419)
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N/A | N/A | N/A |
Precision Descriptor Notes: | Precision and accuracy values were determined using single laboratory data from eight replicate analyses of reagent water fortified with the analytes of interest. NOTES: (1) Total trihalomethanes (TTHMs) is a regulatory parameter representing the sum of multiple trihalomethanes. See the data for specific trihalomethanes for performance information. (2) The samples were preserved with NH4Cl. Additional data is available in the method for samples preserved with Na2SO3, and for different matrix types and analyte concentrations. |
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Detection Level Note: | MDLs were determined using the standard deviation of 8 replicate analyses of an analyte-fortified reagent water sample multiplied by the t-value for 7 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 |
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Revision 1.0, 1995 |