ASTM C1301-1995(2009)e1 Standard Test Method for Major and Trace Elements in Limestone and Lime by Inductively Coupled Plasma-Atomic Emission Spectroscopy (ICP) and Atomic Absorpti.pdf

1、Designation: C 1301 95 (Reapproved 2009)1Standard Test Method forMajor and Trace Elements in Limestone and Lime byInductively Coupled Plasma-Atomic Emission Spectroscopy(ICP) and Atomic Absorption (AA)1This standard is issued under the fixed designation C 1301; the number immediately following the d

2、esignation indicates the 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 () indicates an editorial change since the last revision or reapproval.1NOTEA units statement was added editor

3、ially as new paragraph 1.3 and subsequent paragraphs were renumbered in June2009.1. Scope1.1 The following test method covers the use of inductivelycoupled plasma-atomic emission spectroscopy (ICP) andatomic absorption spectroscopy (AA) in the analysis of majorand trace elements in limestone and lim

4、e (calcined limestone).1.2 Table 1 lists some of the elements that can be analyzedby this test method and the preferred wavelengths. Also seeU.S. EPA Methods 200.7 and 200.9.1.3 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.

5、4 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. Referenced Doc

6、uments2.1 ASTM Standards:2C51 Terminology Relating to Lime and Limestone (as usedby the Industry)D 1193 Specification for Reagent WaterE 135 Terminology Relating to Analytical Chemistry forMetals, Ores, and Related MaterialsE 863 Practice for Describing Atomic Absorption Spectro-metric Equipment3E 1

7、479 Practice for Describing and Specifying Inductively-Coupled Plasma Atomic Emission Spectrometers2.2 U.S. EPA Standards:Methods for the Determination of Metals in EnvironmentalSamples; U.S. EPA Methods 200.2, 200.7, and200.9; Smoley, C. K., 19924Method 6010, Inductively Coupled Plasma Method, SW-8

8、46, Test Methods for Evaluating Solid Waste51This test method is under the jurisdiction of ASTM Committee C07 on Limeand is the direct responsibility of Subcommittee C07.05 on Chemical TestsCurrent edition approved June 1, 2009. Published September 2009. Originallyapproved in 1995. Last previous edi

9、tion approved in 2001 as C 1301 95(2001).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.3Withdrawn. The last

10、 approved version of this historical standard is referencedon www.astm.org.4Available from CRC Press, 2000 Corporate Blvd., N. W., Boca Raton, FL33431.5Available from U.S. Government Printing Office, Washington, DC 20402.TABLE 1 Elements and Some Suggested WavelengthsAMajor Elements ICP Wavelength,

11、nm AA Wavelength, nmCalcium 317.933 (315.887)B422.7Magnesium 279.079 (285.213) 285.2Silicon 251.611 (288.160) 251.6Aluminum 308.215 (309.271) 309.3Iron 259.940 248.3Manganese 257.610 279.5Sodium 588.995 (589.59) 589.0Potassium 766.491 766.5Phosphorus 214.914 (213.618) .CStrontium 421.552 460.7Trace

12、Elements ICP Wavelength, nm AA Wavelength, nmAntimony 206.833 217.6Arsenic 193.696 193.7Barium 455.403 (493.409) 553.6Beryllium 313.042 234.9Boron 249.773 249.8Cadmium 226.502 (228.80) 228.8Chromium 267.716 (205.552) 357.9Cobalt 228.616 240.7 (242.5)Copper 324.754 324.8Lead 220.353 217.0 (283.3)Moly

13、bdenum 202.030 (203.844) 313.3Nickel 231.604 (221.647) 232.0Selenium 196.090 196.0Silver 328.068 328.1Sulfur 180.731 (180.669) .CThallium 190.864 276.8Tin 189.989 235.5 (286.3)Vanadium 292.402 318.4Zinc 213.856 (202.551) 213.9AThe suggested wavelengths may vary for your particular instrument.BNumber

14、s in parentheses are alternate wavelengths.CNot recommended or not used.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.3. Terminology3.1 DefinitionsDefinitions for terms used in this testmethod can be found in Terminologies C 51 and

15、 E 135.3.2 Additional Definitions:3.2.1 total recoverable, ntrace element concentration inan unfiltered sample after heating in acid.3.2.2 total digestion, ncomplete digestion of a sample,including silica and silicate minerals, using the fusion-fluxmethod.4. Summary of Test Method4.1 A sample, diges

16、ted by either fusion or acid, is atomizedand passed into an excitation medium (a plasma in the case ofICP; a flame in the case ofAA). The resulting ions are analyzedby atomic spectroscopy. Elemental concentrations are deter-mined by graphically relating the emission/absorption at spe-cific wavelengt

17、hs for an unknown sample to analytical curvesmade from reference standards of known composition.5. Significance and Use5.1 The presence and concentration of elements in lime andlimestone is important in determining product quality and itssuitability for various uses. This test method provides a mean

18、sof measuring the major and trace element concentration in limeand limestone.6. Interferences6.1 ChemicalChemical interferences, most common inAA, arise from the formation of molecular compounds thatcause absorbances at the wavelength of interest. This molecu-lar band spectral overlap can be minimiz

19、ed by buffering thesample with matrix modifiers (a Lanthanum additive, forexample), using standard additions techniques, matrix match-ing or by careful selection of operating conditions (for ex-ample, using a hotter nitrous oxide/acetylene flame, selectingan alternate wavelength).6.2 PhysicalPhysica

20、l interferences are the result of theinconsistencies in the introduction of the sample into theinstrument, namely the transport and atomization/nebulizationof the sample. These inconsistencies are a function of changingviscosity and surface tension, and are found primarily insamples of high-dissolve

21、d solids or high-acid concentrations.Physical interferences can be reduced by diluting the sampleand by the use of a peristaltic pump.6.3 SpectralSpectral interference, most common in ICP,consists of overlapping and unresolved peaks. Computer soft-ware, along with the analysis of the suspected inter

22、feringelement, can compensate for this effect. Using an alternatewavelength is also a solution. Another spectral interference iscaused by background, both stray light and continuous spec-trum (continuous argon spectrum, for example). Backgroundcorrection adjacent to the analyte line will correct bac

23、kgroundspectral interference.7. Apparatus7.1 Spectrometer.7.1.1 Inductively Coupled Plasma Emission Spectrometer(ICP)Either a scanning sequential or multi-element simulta-neous type ICP, with resolution appropriate for the elements tobe analyzed. The optical path may be in air, vacuum or an inertgas

24、. A detailed description of an ICP is given in PracticeE 1479.7.1.2 Atomic Absorption Spectrometer (AA)An atomicabsorption spectrometer consisting of single or double beamoptics, a monochromator, photomultiplier detector, adjustableslits, a wavelength range from 190 to 800 nm, and provisionsfor inte

25、rfacing with either a strip chart recorder or a computer.A simultaneous background correction system is also recom-mended. A detailed description of an AA is given in PracticeE 863.7.1.2.1 Hollow Cathode LampsSingle hollow cathodelamps, one for each element. Multi-element hollow cathodelamps can be

26、used but spectral interferences are possible.8. Reagents8.1 Purity of ReagentsReagents should conform to thespecifications of the Committee on Analytical Reagents of theAmerican Chemical Society as a minimum when such speci-fications are available.6The high sensitivity of both the ICPandAAmay requir

27、e reagents of high purity. It is recommendedthat the reagents be of sufficiently high purity so as not tolessen the accuracy of the determination.8.2 Purity of WaterAt minimum, water should conform toType II of Specification D 1193.8.3 Stock SolutionsStandard stock solutions may be pur-chased or pre

28、pared from high purity metals or metal salts(Method 6010, SW-846; EPA Methods 200.7 and 200.9). Saltsshould be dried at 105C for 1 h, unless otherwise specified.8.4 Multi-element Calibration StandardsICP calibrationis most often performed using multi-element calibration stan-dards prepared from sing

29、le element stock solutions. Prior topreparing the mixed standards, each stock solution should beanalyzed separately to determine possible spectral interferenceor the presence of impurities. Standards are combined in sucha way that they are chemically compatible (no precipitationoccurs) and do not ca

30、use spectral interferences. An example ofmulti-element combinations is given in EPA Method 200.7.8.5 Interference Check SampleInterference checksamples are made from single element stock solutions at aconcentration level equal to that of the samples to be analyzed.8.6 Calibration BlankA calibration

31、blank is prepared atthe same acid strength as that of the samples to be analyzed;usually 5 or 10 %. To prepare a 10 % nitric acid calibrationblank, add one volume of nitric acid to nine volumes of water.This same blank can be used as the rinse solution for flushingthe system between standards and sa

32、mples.8.7 Reagent BlankThe reagent blank contains all thereagents in the same concentrations (including nitric acid) asthe samples to be analyzed. The reagent blank is carriedthrough the same processes as a sample for analysis.6Reagent Chemicals, American Chemical Society Specifications, AmericanChe

33、mical Society, Washington, DC. For suggestions on the testing of reagents notlisted by the American Chemical Society, see Analar Standards for LaboratoryChemicals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeiaand National Formulary, U.S. Pharmacopeial Convention, Inc. (USPC), Roc

34、kville,MD.C 1301 95 (2009)128.8 Nitric AcidHigh purity nitric acid is recommended.8.9 Lithium Tetraborate (Li2B4O7) Powder or LithiumMetaborate (LiBO2) Powder.8.10 Non-Wetting AgentSaturated solution of HydrogenBromide (HBr), Potassium Bromide (KBr) or Potassium Iodide(KI) as a non-wetting agent to

35、prevent the flux from sticking tothe crucible.8.11 Lanthanum Chloride (LaCl3) PowderLanthanum isadded to samples for AA analysis as a releasing agent (forCalcium) and ionization suppressant (for Aluminum). Whenadded to the sample solution, Lanthanum will preferentiallyreact with potential interferen

36、ts and “release” the analyte. Inaddition, the Lanthanum will preferentially ionize relative toAluminum, aiding in the number of ground state Aluminumatoms. A typical Lanthanum additive is prepared by dissolving175 g LaCl3 in 1 L of water (equivalent to 100 g/L Lantha-num).9. Preparation of Apparatus

37、9.1 Prepare and operate the spectrometer in accordance withthe manufacturers instructions. The present method assumesthat good operating procedures are followed. Design differ-ences between spectrometers make it impractical to specify therequired steps in detail here.10. Calibration and Standardizat

38、ion10.1 Allow a warm-up time of at least 30 min. Operate thespectrometer according to the operation manual for the instru-ment.10.2 Calibrate the instrument by aspirating the blank andstandards. A 10 % by volume HNO3rinse solution is aspiratedfor a minimum of 60 s between each standard. Most newsyst

39、ems are controlled by computer. The computer will estab-lish the slope, intercept and correlation coefficients for eachelement. Some suggested wavelengths are given in Table 1 andEPA Methods 200.2, 200.7, and 200.9.10.3 A peristaltic pump is recommended for aspiratingstandards and samples. The peris

40、taltic pump will reducephysical interferences caused by changes in specimen viscosityand concentration (transport processes).11. Sample Preparation11.1 Major ElementsSamples for major element analysisare prepared for total digestion using lithium tetraborate orlithium metaborate as a flux. Major ele

41、ments include Calcium,Magnesium, Silicon,Aluminum, Iron, Manganese, Sodium andPotassium. Trace elements such as Lead, Arsenic, Seleniumand Antimony will partially volatilize using this fusion methodand it is therefore not recommended for trace element analysis.11.1.1 Take a representative minus 100

42、mesh sample splitand dry at 105C for 2 h.11.1.2 Weigh 0.25 g of dried sample in a graphite orplatinum crucible. Then weigh 1.00 g of lithium metaborate inthe crucible. Add a few drops of non-wetting agent if needed.Mix the sample and lithium metaborate (the flux) well. Coverthe mixed sample-lithium

43、metaborate with an additional 0.50 gof lithium metaborate. This will give a total sample-flux ratioof 1:6.11.1.3 Place a lid (optional) on the crucible prepared in11.1.2 and place in a muffle furnace at 1000C for 30 min.Gently agitate the molten contents of the crucible at least onceduring the 30 mi

44、n heating.11.1.4 Add 12.5 mL of concentrated nitric acid and 40 mLof water to a clean 250 mL wide-mouth plastic bottle.11.1.5 When the 30 min heating in 11.1.3 is complete,quickly pour molten contents of the crucible into the plasticbottle described in 11.1.4. The water will bubble and sizzle.Quickl

45、y put the lid on the plastic bottle and shake. To aid indigestion place the bottle in a warm ultrasonic bath.11.1.6 The contents of the plastic bottle can either bequantitatively transferred to a 250 mL volumetric flask anddiluted to volume or diluted to volume by weight (that is, 1mL = 1 g) in the

46、same 250 mL plastic bottle it was digested in.Keep in mind, however, that the standards need to be made inthe same manner as the samples. Add 10 mL Lanthanumadditive to samples for AA analysis (10 mL addition is part ofthe dilution to volume). Filtering is not necessary.11.2 Trace ElementsSamples fo

47、r trace element analysisare prepared using hydrochloric acid (1:5 or 1+4) and nitricacid (1:2 or 1+1). The trace elements concentrations deter-mined by this method are termed “total recoverable” (that is,components not digested in hot acid are not recovered). Traceelements include, but are not limit

48、ed to, Antimony, Arsenic,Barium, Beryllium, Boron, Cadmium, Chromium, Cobalt,Copper, Lead, Molybdenum, Nickel, Selenium, Silver, Stron-tium, Thallium, Tin, Vanadium, and Zinc.11.2.1 Take a representative minus 100 mesh sample splitand dry at 105C for 2 h.11.2.2 Weigh 1.00 g of dried sample and trans

49、fer to a cleanbeaker.11.2.3 Add 10 mL of dilute hydrochloric acid (see 11.2) and4 mL of dilute nitric acid (see 11.2). In the case of limestone,add the acids slowly so that the powdered sample will notsplatter on the sides of the beaker during its effervescentreaction with the acid. Cover the sample (a ribbed watch glassis best) and place on a hot plate. Heat at approximately 85Cfor 30 min. Boiling should be kept to a minimum.After 30 minallow the sample to cool. Then quantitatively transfer the liquidand any undissolved residue to a 100 mL volumetr