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The D3865-09 (Reapproved 2015) standard specifies a rigorous radiochemical test method for the determination of alpha-particle-emitting plutonium isotopes (²³⁸Pu and ²³⁹/²⁴⁰Pu) in water. The method achieves a minimum detectable concentration of 0.01 Bq/L (0.3 pCi/L) using a one-liter sample volume. It is applicable to both soluble plutonium and plutonium associated with suspended particulate matter, with the latter requiring a rigorous acid dissolution step employing concentrated nitric, hydrofluoric, and hydrochloric acids to ensure total dissolution. Due to the overlapping alpha energies of ²³⁹Pu (5.156 MeV) and ²⁴⁰Pu (5.168 MeV), the standard explicitly states that these two isotopes cannot be distinguished by this method and are reported as a combined activity concentration.
The analytical procedure follows a well-established four-step radiochemical pathway. The water sample is first acidified, and a known activity of a plutonium isotopic tracer (²³⁶Pu or ²⁴²Pu) is added to monitor radiochemical yield. Iron(III) is added, and the plutonium is coprecipitated with ferric hydroxide. After decantation and centrifugation, the precipitate is dissolved and the solution is adjusted to 8 M HNO₃ for purification via anion exchange chromatography. This step provides a highly selective separation of plutonium from other alpha-emitting radionuclides and matrix constituents. Finally, the purified plutonium is electrodeposited onto a polished stainless steel disk in accordance with Practice C1284 for mounting and counting.
The electrodeposited disk is analyzed by alpha pulse-height analysis using a silicon surface barrier or ion-implanted detector. Absolute activities of ²³⁸Pu and ²³⁹/²⁴⁰Pu are calculated independent of discrete detector efficiency and chemical yield corrections by directly comparing the net counts in the isotope peaks relative to the known activity of the added tracer. A significant potential interference is ²²⁸Thorium, which can have coincident alpha energies with the plutonium isotopes of interest if not fully removed during the separation chemistry.
| 🟦 Isotope | ⚡ Alpha Energy (MeV) | 🎯 Role |
|---|---|---|
| ²³⁶Pu | 5.768 | Yield Tracer |
| ²³⁸Pu | 5.499 | Analyte |
| ²³⁹Pu / ²⁴⁰Pu | 5.156 / 5.168 | Analyte (Combined) |
| ²⁴²Pu | 4.901 | Yield Tracer |
| 📐 Parameter | 🔬 Specification |
|---|---|
| Minimum Detectable Concentration | 0.01 Bq/L (0.3 pCi/L) |
| Sample Volume | 1 Liter |
| Core Separation Techniques | Fe(OH)₃ Coprecipitation ➔ Anion Exchange ➔ Electrodeposition |
| Anion Exchange Medium | 8 M HNO₃ |
| Detector Type | Silicon Surface Barrier or Ion-Implanted |
🔍 What is the required detection limit of this test method?
The method is validated to reliably achieve a minimum detectable concentration of 0.01 Bq/L (0.3 pCi/L) for alpha-emitting plutonium isotopes from a one-liter water sample.
💡 Can this method distinguish between ²³⁹Pu and ²⁴⁰Pu?
No. The alpha-particle energies of ²³⁹Pu (5.156 MeV) and ²⁴⁰Pu (5.168 MeV) are too close for standard alpha pulse-height analysis to resolve. The standard explicitly states that due to these overlapping energies, they are reported as a combined ²³⁹/²⁴⁰Pu activity concentration.
⚡ What is the purpose of adding a tracer like ²³⁶Pu or ²⁴²Pu?
The isotopic tracer is added to the sample at the very beginning of the analysis. Because it undergoes the exact same chemical separations as the plutonium in the sample, comparing the net count rate of the tracer’s alpha peak to the known activity added allows the method to automatically correct for both radiochemical yield losses and detector counting efficiency.
📌 How is Plutonium in suspended particulate matter handled?
If the sample contains an insoluble residue that does not dissolve after the initial ferric hydroxide dissolution, the standard specifies a rigorous acid dissolution step. This employs concentrated nitric, hydrofluoric, and hydrochloric acids to completely break down the matrix and ensure all plutonium is fully dissolved and available for the anion exchange separation.