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This test method, designated as ASTM D5316-98 (Reapproved 2024), outlines a procedure for the determination of 1,2-dibromoethane (EDB) and 1,2-dibromo-3-chloropropane (DBCP) in water. It relies on a liquid-liquid microextraction technique coupled with gas-liquid chromatography to achieve a minimum detection level of 0.010 µg/L. This standard is specifically validated for use with drinking waters and groundwaters. Practitioners should note that similar analytical information can be found in EPA Method 504.
The analytical sequence begins with the microextraction of a sample aliquot using hexane as the organic solvent. An injection volume of precisely 2 µL of the resulting hexane extract is then introduced into a gas chromatograph. The instrument must be equipped with a linearized electron capture detector (ECD), which provides the necessary specificity and sensitivity for detecting these halogenated organic compounds at trace concentrations.
A cornerstone of the method’s quality assurance protocol is the handling of calibration standards. Aqueous calibration standards are prepared and subjected to the exact liquid-liquid extraction procedure as the unknown samples. This identical treatment allows the method to naturally compensate for any potential analyte losses or partitioning inefficiencies during the extraction process.
| 🟦 Parameter | 📐 Specification |
|---|---|
| Target Analytes | 1,2-Dibromoethane (EDB) & 1,2-Dibromo-3-chloropropane (DBCP) |
| Minimum Detection Level (MDL) | 0.010 µg/L |
| Extraction Solvent | Hexane |
| Injection Volume | 2 µL |
| Detector Type | Linearized Electron Capture Detector (ECD) |
| Validated Matrices | Drinking water and Groundwater |
The standard mandates that it is the user’s responsibility to ensure the validity of this test method for waters of untested matrices, as the provided performance data is based on reagent water and groundwater studies. Reagent water conforming to ASTM D1193 specifications is required for the preparation of blanks and standards. Laboratories conducting this analysis should adhere to the laboratory management practices outlined in ASTM D3856 to ensure data defensibility.
| 📑 Referenced Document | 🎯 Relevance to Method |
|---|---|
| ASTM D1129 | Standard Terminology Relating to Water |
| ASTM D1193 | Specification for Reagent Water |
| EPA Method 504 | Parallel method for organic compounds in drinking water |
| EPA Method 524 | Measurement of Purgeable Organic Compounds by GC/MS |
🔍 What is the minimum detection level for EDB and DBCP specified in this standard?
The stated minimum detection level for both 1,2-dibromoethane (EDB) and 1,2-dibromo-3-chloropropane (DBCP) in water using this method is 0.010 µg/L.
💡 What type of detector is required for the gas chromatographic analysis?
The standard specifically requires the use of a linearized electron capture detector (ECD) to achieve the necessary sensitivity for the halogenated compounds being analyzed.
⚡ Can this test method be applied to the analysis of wastewater samples?
No. The scope of the standard explicitly states that it is not recommended for wastewaters due to the high risk of interferences from the complex mixture of extractable organic compounds present in such matrices.
📌 Why must the aqueous calibration standards be extracted in the same manner as the samples?
Extracting the calibration standards in an identical fashion to the samples allows the analytical method to directly compensate for extraction losses and other variables inherent to the liquid-liquid microextraction procedure, leading to more reliable quantitative results.