ASTM C1561-2003 Standard Guide for Determination of Plutonium and Neptunium in Uranium Hexafluoride by Alpha Spectrometry《Alpha光谱测定法测量六氟环氧丙烷铀中钚和镎的标准指南》.pdf
《ASTM C1561-2003 Standard Guide for Determination of Plutonium and Neptunium in Uranium Hexafluoride by Alpha Spectrometry《Alpha光谱测定法测量六氟环氧丙烷铀中钚和镎的标准指南》.pdf》由会员分享,可在线阅读,更多相关《ASTM C1561-2003 Standard Guide for Determination of Plutonium and Neptunium in Uranium Hexafluoride by Alpha Spectrometry《Alpha光谱测定法测量六氟环氧丙烷铀中钚和镎的标准指南》.pdf(4页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: C 1561 03Standard Guide forDetermination of Plutonium and Neptunium in UraniumHexafluoride by Alpha Spectrometry1This standard is issued under the fixed designation C 1561; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revisio
2、n, the year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.1. Scope1.1 This method covers the determination of plutonium andneptunium isotopes in uranium hexafluoride by alp
3、ha spectros-copy. The method could also be applicable to any matrix thatmay be converted to a nitric acid system.1.2 This standard does not purport to address all of thesafety concerns, if any, associated with its use. It is theresponsibility of the user of this standard to establish appro-priate sa
4、fety and health practices and determine the applica-bility of regulatory requirements prior to use.2. Referenced Documents2.1 ASTM Standards:C 787 Specification for Uranium Hexafluoride for Enrich-ment2C 996 Specification for Uranium Hexafluoride Enriched toLess Than 5 % 235-U2C 1163 Test Method for
5、 Mounting Actinides for AlphaSpectrometry Using Neodymium Fluoride2C 1475 Guide for the Determination of Neptunium-237 inSoil2D 1193 Specification for Reagent Water3D 3084 Practice for Alpha-Particle Spectrometry of Water4D 3648 Practices for the Measurement of Radioactivity43. Terminology3.1 reagen
6、t blankDI water processed the same as thesamples; used in the determination of the minimum detectableactivity.3.2 region-of-interest (ROI)the channels, or region, in thealpha spectra in which the counts due to a specific radioisotopeappear on a functioning calibrated alpha spectrometry system.4. Sum
7、mary of Test Method4.1 An aliquot of hydrolyzed uranium hexafluoride equiva-lent to approximately 0.5 g of uranium is converted to an oxalicacid-nitric acid system and the uranium is selectively removedvia solid phase extraction. Plutonium and neptunium arefurther purified by additional solid phase
8、extractions. Theplutonium and neptunium are then co-precipitated with neody-mium as the fluorides and counted by alpha spectrometry.4.2 Tracer recoveries using this method are typically be-tween 75 and 90 %. The resolution of the tracer is typically lessthan 40 keV full-width at half-maximum.4.3 The
9、 minimum detectable activity will vary with tracerrecovery, sample size, instrument background, and countingefficiency.5. Significance and Use5.1 The method is applicable to the analysis of materials todemonstrate compliance with the specifications set forth inSpecifications C 787 and C 996.6. Inter
10、ferences6.1 Incomplete removal of U-234 from the neptuniumfraction could result in a false positive for the Np-237 analysis.The method has been shown to adequately remove uranium atenrichments up to 5 %. If the method is used for the analysis ofmaterials at greater than 5 % enrichment, a blank consi
11、sting ofuranium at the same enrichment as the samples should beanalyzed to show adequate removal of the U-234.6.2 A Pu tracer is used to monitor the chemical recovery ofthe Np. Spiked analyses should be performed to confirm theappropriateness of this correction; fractionation of Np and Puduring the
12、separation could lead to incorrect test results.7. Instrumentation7.1 Alpha Spectrometry SystemSee Practices D 3084 andD 3648 for a description of the apparatus.8. Apparatus8.1 Ion Exchange Columns, able to hold a 10 mL resin bedand 15 mL solution washes.1This test method is under the jurisdiction o
13、f ASTM Committee C26 on NuclearFuel Cycle and is the direct responsibility of Subcommittee C26.05 on Methods ofTest.Current edition approved Feb 10, 2003. Published March 2003.2Annual Book of ASTM Standards, Vol 12.01.3Annual Book of ASTM Standards, Vol 11.01.4Annual Book of ASTM Standards, Vol 11.0
14、2.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.8.2 Filter Paper, 0.1 m pore size, 25-mm diameter, com-patible with HF.59. Reagents and Materials9.1 Purity of ReagentsReagent grade chemicals shall beused in all tests. Unless otherw
15、ise indicated, it is intended thatall reagents shall conform to the specifications of the Commit-tee on Analytical Reagents of the American Chemical Society,where such specifications are available.69.2 Purity of WaterUnless otherwise indicated, referencesto water shall be understood to mean reagent
16、water as definedin Specification D 1193.9.3 Ammonium Oxalate (0.1M)Dissolve 12.4 g ammo-nium oxalate in approximately 500 mL of water and dilute to1L.9.4 Ascorbic Acid Solution (Saturated)Add ascorbic acidto 2M nitric acid while stirring until no more ascorbic acid willdissolve. Prepare fresh when n
17、eeded for use.9.5 Ethanol, ethyl alcohol, absolute (200 proof), denatured.9.6 Hydrochloric Acid (HCl), specific gravity 1.19, concen-trated.9.7 Hydrochloric Acid, 9MAdd 750 mL concentrated HClto 100 mL of water, dilute to a final volume of 1 L.9.8 Hydrochloric Acid, 4MAdd 333 mL of concentratedHCl t
18、o 500 mL of water; dilute to a final volume of 1 L.9.9 Hydrochloric Acid, 1.5MAdd 125 mL of concentratedHCl to 500 mL of water; dilute to a final volume of 1 L.9.10 Hydrochloric Acid, 1MAdd 83 mL of concentratedHCl to 500 mL of water; dilute to a final volume of 1 L.9.11 Hydrofluoric Acid (HF), conc
19、entrated HF, minimumassay 48 %.9.12 Iron (III) Nitrate (10 mg Fe/mL)Dissolve 18.0 g ofFe(NO3)39H2O in 250 mL of water.9.13 Neodymium Chloride (10 mg Nd/mL)Add 25 mLconcentrated HCl to 1.17 g neodymium oxide and heat at100C until dissolved. Allow solution to cool and dilute to 100mL with water.9.14 N
20、eodymium Chloride (100 g Nd/mL)Dilute 1 mLof the 10 mg Nd/mL solution to 100 mL with water.9.15 Nitric Acid (HNO3), concentrated nitric acid, specificgravity 1.42.9.16 Nitric Acid (3M)Add 188 mL concentrated nitricacid to 500 mL of water; dilute to a final volume of 1 L.9.17 Nitric Acid (2M)Add 125
21、mL of concentrated nitricacid to 500 mL of water; dilute to a final volume of 1 L.9.18 Oxalic Acid in 1M HCl (0.1M)Dissolve 12.6 goxalic acid dihydrate in 500 mL of 1M HCl; dilute to a finalvolume of 1 L with 1M HCl.9.19 Oxalic Acid in 2M HNO3(0.1M)Dissolve 12.6 goxalic acid dihydrate in 500 mL of 2
22、M HNO3; dilute to a finalvolume of 1 L with 2M HNO3.9.20 Pu-236 or Pu-242 Tracer, traceable to a national orinternational standard.9.21 Sodium Nitrite (100 mg/mL)Dissolve 500 mgNaNO2in 5 mL water. Prepare fresh when using.9.22 Extraction Chromatography Resin, containingoctylphenyl-N,N-di-isobutyl ca
23、rbamoylphosphine oxide(CMPO) dissolved in tri-n-butyl phosphate (TBP) as theimmobilized extractant.7,89.23 Extraction Chromatography Resin, containing diamylamylphosphonate (DAAP) as the immobilized extractant.9,1010. Calibration and Standardization10.1 The alpha spectrometry units should be calibra
24、ted forenergy, resolution and efficiency according to the manufactur-ers instructions. The background counting rate for the instru-ment should be measured at a frequency determined by theuser. See Practices D 3084 and D 3648 for additional informa-tion.11. Procedure11.1 Uranium Removal:11.1.1 Pipett
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