ASTM C1307-2002(2008) Standard Test Method for Plutonium Assay by Plutonium (III) Diode Array Spectrophotometry《用(III)钚数组分光光度法鉴定钚的标准试验方法》.pdf

《ASTM C1307-2002(2008) Standard Test Method for Plutonium Assay by Plutonium (III) Diode Array Spectrophotometry《用(III)钚数组分光光度法鉴定钚的标准试验方法》.pdf》由会员分享，可在线阅读，更多相关《ASTM C1307-2002(2008) Standard Test Method for Plutonium Assay by Plutonium (III) Diode Array Spectrophotometry《用(III)钚数组分光光度法鉴定钚的标准试验方法》.pdf（6页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: C 1307 02 (Reapproved 2008)Standard Test Method forPlutonium Assay by Plutonium (III) Diode ArraySpectrophotometry1This standard is issued under the fixed designation C 1307; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revis

2、ion, 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 test method describes the determination of totalplutonium as plutonium(III) in nitrate and chlor

3、ide solutions.The technique is applicable to solutions of plutonium dioxidepowders and pellets (Test Methods C 697), nuclear grademixed oxides (Test Methods C 698), plutonium metal (TestMethods C 758), and plutonium nitrate solutions (Test Meth-ods C 759). Solid samples are dissolved using the appro

4、priatedissolution techniques described in Practice C 1168. The use ofthis technique for other plutonium-bearing materials has beenreported (1-5), but final determination of applicability must bemade by the user. The applicable concentration range forplutonium sample solutions is 10200 g Pu/L.21.2 Th

5、e values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.3 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-pria

6、te safety and health practices and determine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:3C 697 Test Methods for Chemical, Mass Spectrometric, andSpectrochemical Analysis of Nuclear-Grade PlutoniumDioxide Powders and PelletsC 698 Test Methods f

7、or Chemical, Mass Spectrometric, andSpectrochemicalAnalysis of Nuclear-Grade Mixed Oxides(U, Pu)O2)C 757 Specification for Nuclear-Grade Plutonium DioxidePowder, SinterableC 758 Test Methods for Chemical, Mass Spectrometric,Spectrochemical, Nuclear, and Radiochemical Analysis ofNuclear-Grade Plutoni

8、um MetalC 759 Test Methods for Chemical, Mass Spectrometric,Spectrochemical, Nuclear, and Radiochemical Analysis ofNuclear-Grade Plutonium Nitrate SolutionsC 833 Specification for Sintered (Uranium-Plutonium) Di-oxide PelletsC 1168 Practice for Preparation and Dissolution of Pluto-nium Materials for

9、 Analysis3. Summary of Method3.1 In a diode array spectrophotometric measurement, as ina conventional spectrophotometric measurement, the substancebeing determined absorbs light at frequencies characteristic ofthat substance. The amount of light absorbed at each wave-length is directly proportional

10、to the concentration of thespecies of interest. The absorption is a function of the oxidationstate and the complexation obtained in the solution matrixselected for measurement. Beers Law permits quantifying thespecies of interest relative to a traceable standard when bothsolutions are measured under

11、 the same conditions. The array ofphotosensitive diodes permits the (virtually) simultaneouscollection of spectral information over the entire range of theinstrument, for example, 190820 nm (or any selected portionof the range).An entire absorption spectrum can be obtained in0.1 s; however, optimum

12、precision is obtained from multiplespectra collected over a 4-s period.3.2 Reduction to plutonium(III) is accomplished by theaddition of a measured quantity of reductant solution to thesample aliquant.3.2.1 For nitrate solutions, ferrous sulfamate is the recom-mended reductant. Aliquants (1 mL or le

13、ss) of the samplesolution are diluted with 10 mL of a ferrous reductant/matrixsolution to 1 g Pu/L, and measured.1This test method is under the jurisdiction of ASTM Committee C26 on NuclearFuel Cycle and is the direct responsibility of Subcommittee C26.05 on Methods ofTest.Current edition approved J

14、une 1, 2008. Published July 2008. Originally approvedin 1995. Last previous edition approved in 2002 as C 1307 02.2For solid samples, select the sample size and dissolved solution weight to yieldsample solutions in the 1030 g Pu/L range. With special preparation and spectralanalysis techniques, the

15、method has been applied to nitrate solutions in the 0.110g Pu/L range.3For 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

16、 website.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.3.2.2 For chloride solutions, ascorbic acid is the recom-mended reductant. Aliquants of the sample solution, eachcontaining 50100 mg of plutonium, are diluted with 2 mL ofzirco

17、nium solution to complex fluoride ions, 2 mL ascorbicacid reductant solution, and 1.0 M HCl to a total volume of 25mL, yielding 24 g Pu/L solutions for measurement.3.3 Plutonium concentration is determined from light ab-sorption measurements taken on the sample solution in theblue-green region from

18、516 to 640 nm where a broad doubletband is observed. Spectral quantifying software capable offitting the sample spectrum with spectral information fromstandard solutions is used to calculate the plutonium concen-tration. Both commercially available (6) and custom-designed(7-12) spectral fitting soft

19、ware have been developed whichmay be used for plutonium measurements. The users of thisprocedure are responsible for selecting or customizing, or both,the spectral fitting (and instrument control) software that bestmeets their individual measurement methodology and needs.Software selection will dict

20、ate many of the procedural specificsnot included in this procedure. This procedure is intended toaddress key measurement requirements and to allow usersdiscretion in establishing appropriate procedural details andtechnique variations. The software package selected shouldinclude a feature that indica

21、tes the quality of spectral fit,thereby providing information on the measurement reliabilityand the presence of interferences that absorb light or otherwisealter the plutonium(III) spectrum without requiring supplemen-tal measurements.4. Significance and Use4.1 This test method is designed to determ

22、ine whether agiven material meets the purchasers specification for pluto-nium content.5. Interferences5.1 Materials meeting the applicable material specificationsof theASTM standard for which this procedure was developed,when dissolved and diluted without introduction of interferingcontaminants as d

23、escribed in Practice C 1168, will contain nointerfering elements or species.NOTE 1Fluoride, if present, would interfere if the zirconium, rou-tinely added to the sample solution aliquant for the chloride matrix, wereomitted from the procedure. Zirconium may be added to the nitrate matrix.Ferrous-Red

24、uctant Solution to handle fluorides if present. Zirconium,when used, should be added to all samples, blanks, and standards to obtaina consistent matrix. Refer to Specifications C 833 and C 757.5.2 Interferences are caused by: 1) materials that absorblight in the region of the plutonium absorption, 2

25、) undissolvedsolids that cause light scattering, 3) strong oxidizing orcomplexing agents that prevent complete reduction of theplutonium to the plutonium(III) oxidation state, and 4) anionsthat shift the spectrum.5.2.1 Absorption of light in the region of interest by anotherspecies is a potential in

26、terference. Identification of potentiallyinterfering species and inclusion of their spectra in the spectralcurve fitting process will significantly reduce their effect. At aminimum, sample measurements should be flagged when thehigher than normal fitting error occurs, , resulting from thepresence of

27、 unidentified absorbing species. Enhancement ofthe spectral curve fitting capabilities of the DAS can beachieved by taking double derivatives of the spectrum col-lected. The spectral curve fitting software of the DAS is thenused to quantitate the mathematically manipulated spectrum.NOTE 2Care must b

28、e taken in the choice of the preprocessingmethods (derivatives, mean centering, autoscaling and/or channel selec-tion) as these may affect the robustness of the final model, particularlywith regard to unknown interferences. Use of residual analysis will notalways detect unknown intereferences and re

29、sults will vary depending onthe preprocessing methods and models employed.5.2.2 This spectrophotometric assay method should not beused on turbid (cloudy) solutions or solutions containingundissolved material. In addition to visual or turbidity metermeasurements, or both, the presence of undissolved

30、solids maybe identified by the resulting shifts in the spectral baseline andby elevated spectral fitting errors.NOTE 3Plutonium oxides, mixed oxides, and plutonium metals meet-ing the material specifications for which this test method is intended, willdissolve when procedures in Practice C 1168 are

31、followed. Failure toachieve dissolution is an indication that the material does not meet thespecifications, and the application of this test method for plutonium assaymust be verified by the user. The user and customer are cautioned: whenundissolved solids that persist after exhaustive dissolution e

32、fforts are to beremoved by filtration through filter paper or other inert material ofappropriate porosity, the subsequent plutonium assay measurementsrequire close scrutiny. While filtration of undissolved solids may permitthe reliable measurement of the concentration of plutonium in the filtrate,th

33、e resulting analysis may not be representative of their source material.Solids may indicate incomplete dissolution of the plutonium in the samplematerial, not necessarily a plutonium-free refractory residue. When thistechnique is utilized in support of reprocessing operations, processsolutions conta

34、ining solids may be an indication of incomplete dissolutionof the plutonium-bearing material being processed or of an error inprocess operations. In addition to process control considerations, theundissolved solids may represent accountability and criticality controlproblems.5.2.3 Strong oxidizing a

35、gents and complexing agents insufficient concentration to prevent complete reduction typicallyare not present in plutonium nitrate samples. Appreciableconcentrations of fluoride and sulfate anions have been foundto interfere. The concentration of hydrofluoric acid, added tocatalyze dissolution of ox

36、ides, may be removed by evaporationprior to measurement to ensure that the zirconium effectivelycomplexes the traces of fluoride ion. Changes in the plutoniumspectrum from incomplete reduction due to oxidizing agentsand shifts in the spectrum due to complexing agents are alsoindicated by increases i

37、n the spectral curve fitting error.5.2.4 Anion identity and concentration will shift the loca-tion and alter the shape of the absorption curve. The systemcalibration must include the anion shift effect by encompassingthe expected range of anion identities and concentrations or byusing appropriate sp

38、ectral fitting features that identify andcorrect for the effect.5.3 A study was conducted at the Los Alamos NationalLaboratory to determine the immunity of the Pu(III) spectro-photometric assay method to a diverse species of potentialinterferences. The elements studied were element numbers 1,9, 1113

39、, 17, 19, 2231, 35, 42, 4446, 48, 50, 53, 57, 58, 60,62, 73, 74, 76, 77, 79, 83, 90, 92, 93, and 95. PotentialC 1307 02 (2008)2interference from nitrate, phosphate, sulfate, and oxalic acid isalso documented (13).6. Apparatus6.1 Diode Array Spectrophotometer (DAS)wavelengthrange 190820 nm; wavelengt

40、h accuracy6 2 nm; wavelengthreproducibility 60.05 nm; full dynamic range 0.0022 to 3.3;photometric accuracy at 1 AU with a NBS 931 filter at 512 nmis 60.005 AU; baseline flatness 0.0013 AU; noise at 500 nmis 0.0002AU RMS; stray light measured with a Hoya 056 filterat 220 nm 0.05 %;46.2 Analytical Ba

41、lancereadability of 0.1 mg; linearity 0.1mg over any 10 g range and 0.2 mg over 160 g full scale.6.3 Solution Density Meterreadability of 0.1 mg/mL;precision of 0.3 mg/mL; linearity and accuracy 0.5 mg/mLover the range 0 to 2.0 g/mL.6.4 Adjustable, Fixed-Volume Pipetterscalibrated to de-liver the de

42、sired range of volumes for sample and matrix-reductant solutions.7. Reagents and Materials7.1 Purity of ReagentsReagent grade chemicals shall beused in all tests. Unless otherwise indicated, it is intended thatall reagents conform to the specifications of the Committee onAnalytical Reagents of the A

43、merican Chemical Society wheresuch specifications are available.5Other grades may be used,provided it is first ascertained that the reagent is of sufficientlyhigh purity to permit its use without lessening the accuracy ofthe determination.7.2 Purity of WaterUnless otherwise indicated, referencesto w

44、ater shall be understood to mean distilled or deionizedwater.7.3 Ascorbic Acid-Reductant Solution (C6H8O6, ami-noguanidine bicarbonate (CH6N4H2CO3), 0.4 M in eachreagent)Prepare fresh daily by dissolving7gofascorbicacid and 5.5 g aminoguanidine bicarbonate in 80 mL of 1 MHCl, then dilute to a final

45、volume of 100-mL 1 M HCl.NOTE 4The ascorbic acid is stabilized by the addition of aminoguani-dine (Guanylhydrazine:HN:C(NH2)NHNH2). The stabilized reductantsolution has been found to be effective when ascorbic acid stabilityproblems are encountered.7.4 Ferrous-Reductant Solution (ferrous sulfamate,

46、0.05 M;sulfamic acid, 0.25 M; nitric acid, 1.0 M)Prepare freshweekly by adding 12 mL of freshly prepared ferrous sulfamate(2 M) to 90 mL of sulfamic acid (1.5 M). Stir, then add 175 mLof nitric acid (3.0 M) and dilute to 500 mL with water.7.5 Ferrous Sulfamate (Fe(NH2SO3)2, 2.0 M)Preparefresh for th

47、e preparation of the ferrous-reductant solution. Add220 g of solid sulfamic acid to 450 mL of water, stir, and heatat 7080C until dissolved. Continue stirring and heating,while adding approximately 0.5-g portions of iron metalpowder (Fe0) until 56 g of iron have been dissolved in theheated sulfamic

48、acid. Filter the solution while hot; allow tocool; then dilute to a final volume of 50 mL.NOTE 5The dissolution of the sulfamic acid need not be quantitativebefore beginning the addition of the iron powder. Excessive heatingbeyond the time required to achieve the dissolution of the sulfamicacid/iron

49、 powder or at temperatures above 80C will cause excessivedecomposition of the sulfamic acid7.6 Hydrochloric Acid (HCl, 12 M)Concentrated, sp gr1.19.7.7 Hydrochloric Acid (HCl, 1.0 M)Add 84 mL of hy-drochloric acid (sp gr 1.19) to approximately 500 mL of water.Stir, then dilute to a final volume of 1 L.7.8 Nitric Acid (HNO3, 15.8 M)Concentrated, sp gr 1.42.7.9 Nitric Acid (1.0 M)Add 63 mL of nitric acid (sp gr1.42) to approximately 500 mL of water. Stir, then dilute to afinal volume of 1 L.7.10 Nitric Acid (3.0 M)Add 190 mL of nitric acid (sp gr1.4