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This standard test method D6160-21 provides a two-tiered analytical framework for the determination of polychlorinated biphenyls (PCBs) in waste materials such as oils, sludges, aqueous solutions, and other matrices. Tier I offers rapid screening for PCB presence, while Tier II enables quantification typically within the range of 2 mg/kg to 50 mg/kg. For concentrations exceeding 50 mg/kg, sample dilutions are employed to bring levels within the analytical range. The method adopts a pattern recognition approach using Aroclor reference standards, specifically 1016, 1221, 1232, 1242, 1248, 1254, 1260, 1262, and 1268. Care must be taken with Aroclors 1016, 1232, and 1242 due to potential interferences and weathering effects that can complicate discrimination.
Quantitative results are reported on a dry weight basis, and the quantification limits are dependent on the specific waste stream. The standard emphasizes adherence to safety, health, and environmental practices as per user responsibility.
The primary instrumental technique specified is gas chromatography (GC) with a capillary column and electron capture detector (ECD). The method outlines sample cleanup and instrumental conditions tailored for Aroclor analysis. Alternative detectors such as atomic emission detector (AED) or mass spectrometry (MS) may be utilized provided they demonstrate sufficient performance, particularly in sensitivity. The method references several standard practices including E355, E697, and E1510 for GC and ECD procedures.
Sample preparation and chromatogram interpretation follow the pattern recognition approach, requiring careful comparison with Aroclor standards. Dilution of high-concentration samples is essential for accurate quantification within the Tier II range.
Tier II quantification is optimized for the range of 2 mg/kg to 50 mg/kg. For levels above this range, serial dilutions are necessary to achieve reliable results. The method also cites numerous ASTM standards for supporting procedures, such as D4059 for PCBs in insulating liquids, E203 for water determination, and specifications for volumetric glassware (E288, E969).
| 🟦 Aroclor Standard | 📏 Pattern Characteristics | ⚡ Interference/Weathering Note |
|---|---|---|
| 1016 | Similar to 1242 | Problematic; difficult to distinguish from 1232 and 1242 |
| 1221 | Standard reference | None specified |
| 1232 | Standard reference | Problematic; difficult to distinguish from 1016 and 1242 |
| 1242 | Similar to 1016 | Problematic; difficult to distinguish from 1016 and 1232 |
| 1248 | Standard reference | None specified |
| 1254 | Standard reference | None specified |
| 1260 | Standard reference | None specified |
| 1262 | Standard reference | None specified |
| 1268 | Standard reference | None specified |
| 📏 Parameter | 🎯 Specification |
|---|---|
| Typical quantification range | 2 mg/kg to 50 mg/kg |
| Approach for >50 mg/kg | Sample dilution required |
| Reporting basis | Dry weight of waste sample |
Tier I is designed for rapid screening of waste materials to detect the presence of PCBs without full quantification.
They serve as reference standards for pattern recognition in chromatography. The method specifies nine Aroclor mixtures, with careful attention required for similar patterns.
Yes, atomic emission detection (AED) or mass spectrometry (MS) may be employed if they demonstrate adequate sensitivity and performance.
Quantitative results are reported based on the dry mass of the waste sample, excluding moisture content. Moisture determination methods like E203 may be used.