ASTM D3605-2000(2005) Standard Test Method for Trace Metals in Gas Turbine Fuels by Atomic Absorption and Flame Emission Spectroscopy《用原子吸收和火焰发射光谱法测定燃气涡轮机燃料中痕量金属的试验方法》.pdf

《ASTM D3605-2000(2005) Standard Test Method for Trace Metals in Gas Turbine Fuels by Atomic Absorption and Flame Emission Spectroscopy《用原子吸收和火焰发射光谱法测定燃气涡轮机燃料中痕量金属的试验方法》.pdf》由会员分享，可在线阅读，更多相关《ASTM D3605-2000(2005) Standard Test Method for Trace Metals in Gas Turbine Fuels by Atomic Absorption and Flame Emission Spectroscopy《用原子吸收和火焰发射光谱法测定燃气涡轮机燃料中痕量金属的试验方法》.pdf（4页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D 3605 00 (Reapproved 2005)An American National StandardStandard Test Method forTrace Metals in Gas Turbine Fuels by Atomic Absorptionand Flame Emission Spectroscopy1This standard is issued under the fixed designation D 3605; the number immediately following the designation indicates th

2、e year oforiginal adoption or, in the case of revision, 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 test method covers the determination of sodi

3、um,lead, calcium, and vanadium in Specification D 2880 GradeNos. 1-GT and 2-GT fuels in the range from 0.1 to 2.0 mg/L.This test method is intended for the determination of oil-soluble metals and not waterborne contaminants in oil-watermixtures.1.2 The values stated in SI units are to be regarded as

4、 thestandard.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-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use.2.

5、 Referenced Documents2.1 ASTM Standards:2D 2880 Specification for Gas Turbine Fuel OilsD 4057 Practice for Manual Sampling of Petroleum andPetroleum Products3. Summary of Test Method3.1 The samples are prepared to conform with the require-ments of the method of standard additions, which is selected

6、toobviate problems encountered with the direct analysis oftypical gas turbine fuels that exhibit significant variations inphysical properties. Different, but known, amounts of analyteare added to two portions of sample. These, together with theunaltered sample, are burned in the flame of an atomicab

7、sorption instrument that measures light absorption by theatomized metals. The analysis of the sample portions withadded analyte provides the calibration information necessary tocalculate the analyte content of the unaltered sample.3.2 Lead is determined by atomic absorption in a premixedair-acetylen

8、e flame, and sodium is determined by atomicabsorption or atomic emission in a premixed air-acetyleneflame. Calcium and vanadium are determined by atomicabsorption or atomic emission in a premixed nitrous oxide-acetylene flame.3.3 Most experience with this test method has been in theatomic absorption

9、 mode, although flame emission has beenused successfully. Details in the subsequent sections arewritten for the atomic absorption mode. If the flame emissionmode is used, minor details in the subsequent sections must bealtered to conform to standard practice for flame emissionspectroscopy. The preci

10、sion statement applies only to theatomic absorption mode.NOTE 1Some GT fuel users may wish to determine potassium inaddition to other metals included in this method. Potassium can bedetermined in a manner similar to that for sodium using a potassiumhollow cathode lamp, (unless flame emission mode is

11、 used) a wavelengthof 766.4 mm, and an appropriate organo-potassium standard. Precisiondata for potassium have not been determined.4. Significance and Use4.1 Knowledge of the presence of trace metals in gas turbinefuels enables the user to predict performance and, whennecessary, to take appropriate

12、action to prevent corrosion.5. Apparatus5.1 Atomic Absorption Spectrophotometer, capable of mea-suring radiation over the wavelength range from 280 to 600nm. The instrument must be capable of measuring low-levelsignals (approximately 1 % absorption or 0.004 absorbanceunit per mg/L vanadium). The ins

13、trument should also beequipped as follows.5.1.1 Burner, with variable nebulizer and auxiliary oxidantsupply to reduce non-atomic absorption from unburned hydro-carbons which cause interferences.5.1.1.1 Burner Head, capable of supporting a nitrous oxide-acetylene flame.5.1.1.2 Burner Head, single- or

14、 multiple-slot, capable ofsupporting an air-acetylene flame.5.1.2 Electronic Detection System, capable of reading to thenearest 0.1 % absorption or 0.0004 absorbance.1This test method is under the jurisdiction of ASTM Committee D02 onPetroleum Products and Lubricants and is the direct responsibility

15、 of SubcommitteeD02.03 on Elemental Analysis.Current edition approved May 1, 2005. Published May 2005. Originallyapproved in 1977. Last previous edition approved in 2000 as D 3605 00.2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.

16、org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.5.1.2.1 The text describes the measurement of absorptionsignals

17、 that is, either percent absorption or absorbance. Forinstruments reading in percent absorption, absorption signalsof 0.1 % absorption must be measurable. For instrumentsreading in absorbance, signals of 0.0004 absorbance must bemeasurable.5.1.3 Hollow Cathode Lamp Power Supply, regulated tominimize

18、 drift.5.1.4 Monochromator, capable of resolving the 318.34318.40-nm vanadium doublet from the 318.54-nm vanadiumline.5.1.5 Hollow Cathode Lamps, one each for calcium, so-dium, lead, and vanadium.NOTE 2Electrodeless-discharge lamps can be an acceptable alterna-tive, but the precision of this method

19、was determined with hollow cathodelamps.5.1.6 When the instrument has flame-emission capability,the emission technique can be used for the analyses of sodium,calcium, and vanadium.5.2 Volumetric Flasks, 25-mL.5.3 Glass Vials, 40-mL, screw-cap type, polyethylene-linedcaps.5.4 Syringe, 100-L, Hamilton

20、 type or equivalent.6. Reagents6.1 Purity of ReagentsReagent grade chemicals shall beused in tests. Unless otherwise indicated, it is intended that allreagents conform to the specifications of the Committee onAnalytical Reagents of the American Chemical Society wheresuch specifications are available

21、.3Other grades may be used,provided it is ascertained that the reagent is of sufficiently highpurity to permit its use without lessening the accuracy of thedetermination.6.2 1,2,3,4-tetrahydronaphthalene,4practical grade,analyte-sterile.NOTE 3Analyte-sterile 1,2,3,4-tetrahydronaphthalene can be pre-

22、pared by extracting a portion of tetralin with an equal amount ofhydrochloric acid in a covered screw-cap vial. Heat the vial on a steambath for 1 h and shake the vial for 1 h. If the acid extracted 1,2,3,4-tetrahydronaphthalene and unextracted 1,2,3,4-tetrahydronaphthalenegive indistinguishable abs

23、orption signals for each of the analytes underoptimal experimental conditions, the unextracted 1,2,3,4-tetrahydronaphthalene can be used throughout this method.6.3 Organometallic StandardsOil-soluble salts of sodium,lead, calcium, and vanadium of known concentration.56.4 Mixed StandardPrepare a mixe

24、d standard containing250 mg/L each of sodium, lead, calcium, and vanadium bydissolving the appropriate amounts of organometallic standardsin 1,2,3,4-tetrahydronaphthalene and making the required di-lutions. Prepare fresh daily, as needed.7. Sampling7.1 Samples shall be taken in accordance with the i

25、nstruc-tions in Practice D 4057.8. Procedure8.1 Fill two clean 25-mL volumetric flasks to the line withsample. With the microlitre syringe add 50 L of mixedstandard to one flask and 100 L to the other. Touch the needleof the syringe to the inner wall of the flask to ensurequantitative transfer of th

26、e standard. Invert and mix thecontents. (The two flasks are now spiked with 0.5 mg/L and 1.0mg/L of sodium, lead, calcium, and vanadium). Alternatively,weigh 25.0 g of sample into each of two clean disposable glassvials and add the standard in the same manner. (The two vialsare now spiked with 0.5 m

27、g/kg and 1.0 mg/kg of sodium, lead,calcium, and vanadium.)8.2 Prepare a third spiked sample by adding approximately1 mL of the mixed standard to approximately 25 mL of sample.This solution serves only to aid in establishing satisfactoryoperating conditions for the atomic absorption instrument.8.3 Es

28、tablish the atomic absorption instrument operatingconditions, which are recommended by the manufacturer, andconsider the following special points. Select the mode, flamegases, and spectral lines from the information presented inTable 1.8.4 Analysis:8.4.1 With the atomic absorption instrument in oper

29、ation formonitoring lead absorption and with 1,2,3,4-tetrahydronaphthalene nebulizing, zero the instrument. Aspi-rate into the flame the third spiked sample described in 8.2 andnote the net lead absorption signal. Optimize experimentalconditions by adjusting the burner position (relative to thehollo

30、w cathode beam), the flow rates of the fuel and oxidantgases, and the sample aspiration rate until the net lead3Reagent Chemicals, American Chemical Society Specifications, AmericanChemical Society, Washington, DC. For suggestions on the testing of reagents notlisted by the American Chemical Society

31、, see Analar Standards for LaboratoryChemicals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeiaand National Formulary, U.S. Pharmaceutical Convention, Inc. (USPC), Rockville,MD.4Tetralin (1,2,3,4-tetrahydronaphthalene), manufactured by E. I. duPont deNemours and Co., has been found

32、 satisfactory. If you are aware of alternativesuppliers, please provide this information to ASTM International Headquarters.Your comments will receive careful consideration at a meeting of the responsibletechnical committee1, which you may attend.5Conostan standards, available from Conostan Division

33、, Continental Oil Co.,Ponca City, OK 74601, were used in determining the precision quoted in thismethod. Other standards are available from the Office of Standard ReferenceMaterials, Room B314, Chemistry Bldg., National Institute of Standards andTechnology, Washington, DC 20234, and from Angstrom, I

34、nc., P. O. Box 252,Belleville, MI 48111, but the precision statement may or may not apply to resultsobtained with these standards.TABLE 1 Experimental ConditionsElement Mode Wavelength, nm Fuel OxidantNa Absorption 589.6 C2H2airNa Emission 589.6 C2H2airPb Absorption 283.3 C2H2airCa Absorption 422.7

35、C2H2N2OCa Emission 422.7 C2H2N2OV Absorption 318.34318.40 C2H2N2OV Emission 437.9 C2H2N2OD 3605 00 (2005)2absorption signal maximizes. Re-zero the instrument with1,2,3,4-tetrahydronaphthalene nebulizing, and consecutivelyintroduce into the flame the unaltered sample and the twospiked samples, with 1

36、,2,3,4-tetrahydronaphthalene nebulizingbetween each sample. Record the absorption signal of eachsample and of each blank between samples.8.4.1.1 At optimal experimental conditions, the analyteconcentration that accounts for 1 % absorption should beapproximately 1 mg/L. The percent absorption to conc

37、entrationratio must be near unity in order to achieve the lower limits ofdetection that are required. This note does not apply to flameemission measurements.8.4.2 With the atomic absorption instrument in operation formonitoring vanadium absorption and with 1,2,3,4-tetrahydronaphthalene nebulizing, z

38、ero the instrument. Intro-duce into the flame the third spiked sample described in 8.2.Record the net vanadium absorption signal. Optimize theexperimental conditions as in 8.4.1. Re-zero the instrumentwith 1,2,3,4-tetrahydronaphthalene nebulizing and consecu-tively introduce into the flame the unalt

39、ered sample and the twospiked samples. Record the absorption signal of each sampleand of each 1,2,3,4-tetrahydronaphthalene blank betweensamples.8.4.3 With the atomic absorption instrument in operation formonitoring sodium absorption, zero the instrument with1,2,3,4-tetrahydronaphthalene nebulizing,

40、 and consecutivelyintroduce into the flame the unaltered sample and the twospiked samples. Record the absorption signal of each sampleand of each 1,2,3,4-tetrahydronaphthalene blank betweensamples.NOTE 4For determining sodium and calcium, the maximization ofabsorption or emission signals is not crit

41、ical.8.4.4 With the atomic absorption instrument in operation formonitoring calcium absorption, zero the instrument with1,2,3,4-tetrahydronaphthalene nebulizing, and consecutivelyintroduce into the flame the unaltered sample and the twospiked samples. Record the absorption signal of each sampleand o

42、f each 1,2,3,4-tetrahydronaphthalene blank betweensamples.9. Calculation9.1 For each absorption signal, calculate the net absorptionsignal as follows:a 5 A 2 b11 b2!/2 (1)where:a = net absorption signal,A = observed absorption signal,b1= blank signal before the sample, andb2= blank signal after the

43、sample.NOTE 5Blank corrections are usually small. If a large drift in blanksignals is observed during a series of measurements, some experimentalparameter is out of control. The cause of the variation should be corrected,and the measurements repeated.9.2 For each element in turn, calculate sensitivi

44、ties asfollows:S0.55 2 a12 a2! (2)S1.05 a32 a2! (3)S 5 S0.51 S1.0!/2 (4)where:S0.5= sensitivity for the 0.5-mg/L spiked sample,S1.0= sensitivity for the 1.0-mg/L spiked sample,S = average sensitivity,a1= net absorption signal for the 0.5-mg/L spikedsample,a2= net absorption signal for the unaltered

45、sample, anda3= net absorption signal for the 1.0-mg/L spikedsample.9.3 Calculate the ratio of sensitivities, R, as follows:R 5 S1.0/S0.5(5)If R falls outside the range of 0.90 # R # 1.10, the data arenonlinear. Readjust experimental conditions and repeat theanalysis.9.4 Calculate the concentration o

46、f each element as follows:mg/L 5 a2/S (6)mg/kg 5 a2/S 3 d! (7)where d = density of the sample in g/ml.10. Quality Control Checks (QA/QC)10.1 When QA/QC protocols are already established in thetesting facility, these may be used to confirm the reliability ofthe test method.10.2 Since reference materi

47、als for the various matrices arenot available and the test method utilizes the method ofstandard additions, the only practical quality control check is toverify the accuracy of the organometallic standard in 6.3.Asource independent of this standard should be acquired and asample carried through the

48、analysis using the second-sourcestandard as the known addition. Results of this test can becompared to the original sample result using the originalstandard material to verify accuracy.11. Report11.1 Report results for each element to the nearest 0.1 mg/L.12. Precision and Bias12.1 The precison of t

49、his test method as obtained bystatistical examination of interlaboratory test results is asfollows:12.1.1 RepeatabilityThe difference between successivetest results obtained by the same operator with the sameapparatus under constant operating conditions on identical testmaterial would, in the long run, in the normal and correctoperation of the test method exceed the following values onlyin one case in twenty:Element RepeatabilityV 0.452 (concentration)12Pb 0.244 (concentration)12Ca 0.202 (concentration)12Na 0.232 (concentration)1212.1.2 ReproducibilityThe di