ASTM C1561-2010 Standard Guide for Determination of Plutonium and Neptunium in Uranium Hexafluoride by Alpha Spectrometry《α光谱法测定铀六氟化物中钚和镎的标准指南》.pdf
《ASTM C1561-2010 Standard Guide for Determination of Plutonium and Neptunium in Uranium Hexafluoride by Alpha Spectrometry《α光谱法测定铀六氟化物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 C1561-2010 Standard Guide for Determination of Plutonium and Neptunium in Uranium Hexafluoride by Alpha Spectrometry《α光谱法测定铀六氟化物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: C1561 10Standard Guide forDetermination of Plutonium and Neptunium in UraniumHexafluoride and U-Rich Matrix by Alpha Spectrometry1This standard is issued under the fixed designation C1561; the number immediately following the designation indicates the year oforiginal adoption or, in the
2、 case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon () indicates an editorial change since the last revision or reapproval.1. Scope1.1 This method covers the determination of plutonium andneptunium isotopes in uranium hexa
3、fluoride by alpha spectros-copy. The method can also be applicable to any matrix that maybe 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 ap
4、pro-priate safety and health practices and determine the applica-bility of regulatory requirements prior to use.2. Referenced Documents2.1 ASTM Standards:2C787 Specification for Uranium Hexafluoride for Enrich-mentC996 Specification for Uranium Hexafluoride Enriched toLess Than 5 %235UC1163 Practice
5、 for Mounting Actinides for Alpha Spec-trometry Using Neodymium FluorideC1475 Guide for Determination of Neptunium-237 in SoilD1193 Specification for Reagent WaterD3084 Practice for Alpha-Particle Spectrometry of WaterD3648 Practices for the Measurement of Radioactivity3. Terminology3.1 reagent blan
6、kDI 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. Summary o
7、f 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 extrac
8、tions. 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 % for uranium hexafluoride, for differentmatrix (with impurities): 10 %. The resolution of the tracer
9、 istypically less than 40 keV full-width at half-maximum.4.3 The 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 sp
10、ecifications set forth inSpecifications C787 and C996.5.2 The method can be used to quantify Pu and Np in U-richmatrix before to recycle them.6. Interferences6.1 Incomplete removal of U-234 from the neptuniumfraction could result in a false positive for the Np-237 analysis.The method has been shown
11、to adequately remove uranium atenrichments up to 5 %. If the method is used for the analysis ofmaterials at greater than 5 % enrichment, a blank consisting 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 c
12、hemical recovery ofthe Np. Spiked analyses should be performed to confirm theappropriateness of this correction; fractionation of Np and Puduring the separation could lead to incorrect test results.7. Instrumentation7.1 Alpha Spectrometry SystemSee Practices D3084 andD3648 for a description of the a
13、pparatus.1This guide is under the jurisdiction of ASTM Committee C26 on Nuclear FuelCycle and is the direct responsibility of Subcommittee C26.05 on Methods of Test.Current edition approved Oct. 1, 2010. Published October 2010. Originallyapproved in 2003. Last previous edition approved in 2003 as C1
14、561-03. DOI:10.1520/C1561-10.2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.1Copyright ASTM International, 1
15、00 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.8. Apparatus8.1 Ion Exchange Columns, able to hold a 10 mL resin bedand 15 mL solution washes.8.2 Filter Paper, 0.1 m pore size, 25-mm diameter, com-patible with HF.39. Reagents and Materials9.1 Purity of ReagentsReag
16、ent grade chemicals shall beused in all tests. Unless otherwise 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.49.2 Purity of WaterUnless otherwise indica
17、ted, referencesto water shall be understood to mean reagent water as definedin Specification D1193.9.3 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 unt
18、il no more ascorbic acid willdissolve. Prepare fresh when needed 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
19、 L.9.8 Hydrochloric Acid, 4MAdd 333 mL of concentratedHCl to 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
20、 to a final volume of 1 L.9.11 Hydrofluoric Acid (HF), concentrated 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. A
21、llow solution to cool and dilute to 100mL with water.9.14 Neodymium Chloride (100 g Nd/mL)Dilute 1 mL ofthe 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; di
22、lute to a final volume of 1 L.9.17 Nitric Acid (2M)Add 125 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 g oxalicacid dihydrate in 500 mL of 1M HCl; dilute to a final volumeof 1 L with 1M HCl.9.19 Oxalic Acid in 2M HN
23、O3(0.1M)Dissolve 12.6 goxalic acid dihydrate in 500 mL of 2M 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 Chr
24、omatography Resin, containingoctylphenyl-N,N-di-isobutyl carbamoylphosphine oxide(CMPO) dissolved in tri-n-butyl phosphate (TBP) as theimmobilized extractant.5,69.23 Extraction Chromatography Resin, containing diamylamylphosphonate (DAAP) as the immobilized extractant.7,810. Calibration and Standard
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