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This standard test method, D3373-17, outlines the procedure for determining dissolved and total recoverable vanadium in water and wastewater using graphite furnace atomic absorption spectrophotometry (GFAAS). The method is applicable to a variety of water matrices including reagent water, lake water, tap water, river water, condensate from a medium Btu coal gasification process, and well water. It is optimized for vanadium concentrations between 10 and 200 µg/L based on a 20-µL sample volume, with a reported detection level as low as 4 µg/L. For concentrations exceeding 200 µg/L, proper dilution is recommended.
Users must ensure the method’s validity for untested matrices. The standard also emphasizes adherence to safety protocols and regulatory requirements, as it does not address all safety concerns. All values are expressed in SI units.
The analytical procedure involves graphite furnace atomic absorption spectrophotometry for vanadium analysis. Key steps include sample preparation for dissolved and total recoverable fractions, calibration with standard solutions, and rigorous quality control. The standard defines a continuing calibration blank (CCB) to verify blank response and freedom from carryover, and a continuing calibration verification (CCV) to monitor instrumental drift, with concentrations spanning the calibration range. Referenced standards such as D1066 for steam sampling, D3370 for closed conduit sampling, and D3919 for trace elements in water by GFAAS provide additional procedural guidance.
The method requires careful attention to holding times as per D4841 and spiking techniques as per D5810 to ensure accurate results.
| 🟦 Parameter | 📏 Specification | 📐 Notes |
|---|---|---|
| Optimum Range | 10–200 µg/L | Based on 20-µL injection |
| Detection Level | ≥4 µg/L | Reported achievable |
| High Concentration | >200 µg/L | Dilute samples before analysis |
| Sample Volume | 20 µL | Standard injection volume |
The standard incorporates several quality control practices to ensure reliable results. These include adherence to D2777 for precision and bias assessment, D5847 for quality control specifications, and D5810 for spiking. The method has been validated for specific water types, but users must verify its performance for new matrices. Terminology such as “continuing calibration blank” and “continuing calibration verification” is defined to maintain data integrity.
| 🟦 Standard | 🎯 Focus Area | ⚡ Relevance |
|---|---|---|
| D1066 | Sampling Steam | Applicable for steam condensate sampling |
| D1129 | Terminology | Defines water-related terms |
| D3919 | Trace Elements by GFAAS | Comprehensive practice for GFAAS |
| D5847 | Quality Control | Guidelines for QC specifications |
The optimum range is 10 to 200 µg/L based on a 20-µL sample size. A detection level as low as 4 µg/L has been reported.
Yes, the test method covers most waters and wastewater, including various types like lake water, tap water, and condensate. However, validation is required for untested matrices.
Key measures include continuing calibration blanks (CCB) to check for carryover and continuing calibration verification (CCV) to monitor drift. References to D5847 and D2777 further guide QC practices.
Samples with concentrations above 200 µg/L can be analyzed after proper dilution to bring them within the optimum range.