ASTM D6785-2013 1250 Standard Test Method for Determination of Lead in Workplace Air Using Flame or Graphite Furnace Atomic Absorption Spectrometry《采用火焰或石墨炉原子吸收光谱法测定工作场所空气中铅含量的标准试验.pdf

《ASTM D6785-2013 1250 Standard Test Method for Determination of Lead in Workplace Air Using Flame or Graphite Furnace Atomic Absorption Spectrometry《采用火焰或石墨炉原子吸收光谱法测定工作场所空气中铅含量的标准试验.pdf》由会员分享，可在线阅读，更多相关《ASTM D6785-2013 1250 Standard Test Method for Determination of Lead in Workplace Air Using Flame or Graphite Furnace Atomic Absorption Spectrometry《采用火焰或石墨炉原子吸收光谱法测定工作场所空气中铅含量的标准试验.pdf（17页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D6785 13Standard Test Method forDetermination of Lead in Workplace Air Using Flame orGraphite Furnace Atomic Absorption Spectrometry1This standard is issued under the fixed designation D6785; the number immediately following the designation indicates the year oforiginal adoption or, in

2、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.1. Scope1.1 This standard specifies flame and graphite furnaceatomic absorption spectrometric me

3、thods for the determinationof the time-weighted average mass concentration of particulatelead and lead compounds in workplace air.1.2 The method is applicable to personal sampling of theinhalable fraction of airborne particles, as defined in ISO 7708,and to static (area) sampling.1.3 The sample diss

4、olution procedure specifies hot plate ormicrowave digestion, or ultrasonic extraction (11.2). Thesample dissolution procedure is not effective for all leadcompounds (see Section 5). The use of an alternative, morevigorous dissolution procedure is necessary when it is desiredto extract lead from comp

5、ounds present in the test atmospherethat are insoluble using the dissolution procedures describedherein. For example if it is desired to determine silicate lead, ahydrofluoric acid dissolution procedure is required.1.4 The flame atomic absorption method is applicable to thedetermination of masses of

6、 approximately 1 to 200 g of leadper sample, without dilution (1).2The graphite furnace atomicabsorption method is applicable to the determination of massesof approximately 0.01 to 0.5 g of lead per sample, withoutdilution (1).1.5 The ultrasonic extraction procedure has been validatedfor the determi

7、nation of masses of approximately 20 to 100 gof lead per sample, for laboratory-generated lead fume air filtersamples (2).1.6 The concentration range for lead in air for which thisprocedure is applicable is determined in part by the samplingprocedure selected by the user (see Section 10).1.7 Anions

8、that form precipitates with lead may interfere,but this potential interference is overcome by the addition ofthe disodium salt of ethylenediamine tetraacetic acid (EDTA)when necessary.1.8 The values stated in SI units are to be regarded as thestandard. No other units of measurement are included in t

9、hisstandard.1.9 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.

10、Referenced Documents2.1 ASTM Standards:3D1193 Specification for Reagent WaterD1356 Terminology Relating to Sampling and Analysis ofAtmospheresD3195 Practice for Rotameter CalibrationD4840 Guide for Sample Chain-of-Custody ProceduresD7035 Test Method for Determination of Metals and Met-alloids in Air

11、borne Particulate Matter by InductivelyCoupled Plasma Atomic Emission Spectrometry (ICP-AES)E882 Guide for Accountability and Quality Control in theChemical Analysis LaboratoryE1370 Guide for Air Sampling Strategies for Worker andWorkplace ProtectionE1792 Specification for Wipe Sampling Materials fo

12、r Leadin Surface Dust2.2 Other Standards:4ISO 648 Laboratory GlasswareOne-Mark PipettesISO 1042 Laboratory GlasswareOne-Mark VolumetricFlasksISO 3534-1 StatisticsVocabulary and SymbolsPart 1:General Statistical Terms and Terms Used in Probability1This test method is under the jurisdiction of ASTM Co

13、mmittee D22 on AirQuality and is the direct responsibility of Subcommittee D22.04 on Workplace AirQuality.Current edition approved Oct. 1, 2013. Published October 2013. Originallyapproved in 2002. Last previous edition approved in 2008 as D6785 - 08. DOI:10.1520/D6785-13.2The boldface numbers in par

14、entheses refer to the list of references at the end ofthis standard.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 w

15、ebsite.4Available from American National Standards Institute (ANSI), 25 W. 43rd St.,4th Floor, New York, NY 10036, http:/www.ansi.org.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States1ISO 3585 Glass Plant, Pipelines and FittingsProperti

16、es ofBorosilicate Glass 3.3ISO 6879 Air QualityPerformance Characteristics andRelated Concepts For Air Quality MethodsISO 6955 Analytical Spectroscopic MethodsFlameEmission, Atomic Absorption, and AtomicFluorescenceVocabularyISO 7708 Particle Size Definitions for Health Related Sam-plingISO 15202-2

17、Workplace AirDetermination of Metals andMetalloids in Airborne Particulate Matter by InductivelyCoupled Plasma Atomic Emission SpectrometryPart 2:Sample PreparationISO 13137 Workplace AtmospheresPumps for PersonalSampling of Chemical and Biological AgentsRequirements and Test MethodsEN 482 Workplace

18、 ExposureGeneral Requirements forthe Performance of Procedures for the Measurement ofChemical AgentsEN 689 Workplace AtmospheresGuidance for the Assess-ment of Exposure to Chemical Agents for Comparisonwith Limit Values and Measurement StrategyEN 1232 Workplace AtmospheresPumps for PersonalSampling

19、of Chemical AgentsRequirements and TestEN 1540 Workplace AtmospheresTerminologyEN 12919 Workplace AtmospheresPumps for Samplingof Chemical Agents with a Volume Flow Rate of Over 5L/MinRequirements and Test MethodsEN 13205 Workplace AtmospheresAssessment of Perfor-mance of Instruments for Measurement

20、 of Airborne Par-ticle ConcentrationsEN ISO 8655-1, Piston-Operated Volumetric InstrumentsPart 1: Terminology, General Requirements and UserRecommendationsEN ISO 8655-2 Piston-Operated Volumetric InstrumentsPart 2: Piston PipettesEN ISO 8655-5 Piston-Operated Volumetric InstrumentsPart 5: Dispensers

21、EN ISO 8655-6 Piston-Operated Volumetric InstrumentsPart 6: Gravimetric Test Methods3. Terminology3.1 General DefinitionsFor definitions of other terms usedin this test method, refer to Terminology D1356.3.1.1 breathing zonethe space around the workers facefrom where he or she takes his or her breat

22、h. For technicalpurposes a more precise definition is as follows: hemisphere(generally accepted to be 0.3 m in radius) extending in front ofthe human face, centered on the midpoint of a line joining theears; the base of the hemisphere is a plane through this line, thetop of the head and the larynx.

23、The definition is not applicablewhen respiratory protective equipment is used. EN 15403.1.2 chemical agentany chemical element or compound,on its own or admixed as it occurs in the natural state or asproduced, used or released including release as waste, by anywork activity, whether or not produced

24、intentionally andwhether or not placed on the market. EN 15403.1.3 exposure (by inhalation)a situation in which achemical agent is present in air which is inhaled by a person.3.1.4 occupational exposure limit valuelimit of the time-weighted average of the concentration of a chemical agent inthe air

25、within the breathing zone of a worker in relation to aspecified reference period. EN 15403.1.4.1 DiscussionAn example is the Threshold LimitValue (TLV) for a given substance in workplace air, asestablished by the ACGIH (3).3.1.5 measuring procedureprocedure for sampling andanalyzing one or more chem

26、ical agents in the air and includingstorage and transportation of the sample.3.1.6 operating timethe period during which a samplingpump can be operated at specified flow rate and back pressurewithout recharging or replacing the battery. EN 12323.1.7 reference periodthe specified period of time state

27、dfor the limit value of a specific chemical agent.3.1.7.1 DiscussionExamples of limit values for differentreference periods are short-term and long-term exposure limits,such as those established by the ACGIH (3).3.1.8 time weighted average (TWA) concentration theconcentration of a chemical agent in

28、the atmosphere, averagedover the reference period.3.1.8.1 DiscussionA more detailed discussion of TWAconcentrations and their use can be found in the AmericanConference of Government Industrial Hygienists publicationThreshold Limit Values for Chemical Substances and PhysicalAgents; Biological Exposu

29、re Indices (3).3.1.9 workplacethe defined area or areas in which thework activities are carried out. EN 15403.2 Particle Size Fraction Definitions:3.2.1 inhalable conventiona target specification for sam-pling instruments when the inhalable fraction is of interest.ISO 77083.2.2 inhalable fractionthe

30、 mass fraction of total airborneparticles which is inhaled through the nose and mouth.3.2.2.1 DiscussionThe inhalable fraction depends on thespeed and direction of air movement, on breathing rate andother factors. ISO 77083.3 Sampling Definitions:3.3.1 personal samplera device attached to a person t

31、hatsamples air in the breathing zone. EN 15403.3.2 personal samplingThe process of sampling carriedout using a personal sampler. EN 15403.3.3 sampling instrument; samplerfor the purposes ofthis standard, a device for collecting airborne particles.3.3.3.1 DiscussionInstruments used to collect airborn

32、eparticles are frequently referred to by a number of other terms,for example, sampling heads, filter holders, filter cassettes etc.3.3.4 static sampler; area samplera device, not attachedto a person, used in static (area) sampling.3.3.5 static sampling; area samplingthe process of airsampling carrie

33、d out in a particular location.3.4 Analytical Definitions:D6785 1323.4.1 sample dissolutionthe process of obtaining a solu-tion containing the analytes of interest from a sample. This mayor may not involve complete dissolution of the sample.3.4.2 sample preparationall operations carried out on asamp

34、le, after transportation and storage, to prepare it foranalysis, including transformation of the sample into a mea-surable state, where necessary.3.4.3 sample solutionsolution prepared by the process ofsample dissolution, but possibly needing to be subjected tofurther operations in order to produce

35、a test solution that isready for analysis.3.4.4 test solutionsolution prepared by the process ofsample dissolution and, if necessary, having been subjected toany further operations required to bring it into a state in whichit is ready for analysis.3.5 Statistical Terms:3.5.1 analytical recoveryratio

36、 of the mass of analytemeasured when a sample is analyzed to the known mass ofanalyte in that sample, expressed as a percentage.3.5.2 biasconsistent deviation of the results of a measure-ment process from the true value of the air quality character-istic itself. ISO 68793.5.3 overall uncertainty(of

37、a measuring procedure or ofan instrument) quantity used to characterize as a whole theuncertainty of a result given by an apparatus or measuringprocedure.3.5.4 precisionthe closeness of agreement of results ob-tained by applying the method several times under prescribedconditions. ISO 68793.5.4.1 Di

38、scussionPrecision is often expressed in terms ofthe relative standard deviation.3.5.5 true valuethe value which characterizes a quantityperfectly defined in the conditions which exist when thatquantity is considered. ISO 3534-13.5.5.1 DiscussionThe true value of a quantity is a theo-retical concept

39、and, in general, cannot be known exactly.EN 15404. Summary of Test Method4.1 A known volume of air is drawn through a filter tocollect particulate lead and lead compounds. For personalsampling, a sampler designed to collect the inhalable fractionof airborne particles may be used.4.2 The filter and c

40、ollected sample are subjected to adissolution procedure in order to extract lead. The sampledissolution procedure may use one of three techniques: hotplate digestion, microwave digestion or ultrasonic extraction.4.3 Sample solutions are analyzed for lead content byaspirating into the oxidizing air-a

41、cetylene flame of an atomicabsorption spectrometer equipped with a lead hollow cathodelamp or electrodeless discharge lamp. Absorbance measure-ments are made at 283.3 nm, and analytical results are obtainedby the analytical curve technique.4.4 For accurate lead determination when the concentrationof

42、 lead in the solution is low, the analysis may be repeatedusing graphite furnace atomic absorption spectrometry. Ali-quots of the test solution are injected into a graphite furnace,and after drying and sample ashing stages, the sample isatomized electrothermally. Absorbance measurements aremade at 2

43、83.3 nm with background correction, and results areobtained by the analytical curve technique.4.5 The results may be used for the assessment of workplaceexposures to airborne particulate lead (see Guide E1370 andEN 689).5. Reactions5.1 In general, the overwhelming majority of particulatelead compoun

44、ds that are commonly found in samples ofworkplace air are converted to water-soluble lead ions (Pb2+)by the sample dissolution procedures described in 11.2.However, certain lead compounds, for example lead silicate,might not be dissolved. If necessary, a dissolution procedureemploying hydrofluoric a

45、cid should be used to dissolve silicatelead. If there is any doubt about the effectiveness of theseprocedures for the dissolution of particulate lead compoundsthat may be present in the test atmosphere, then this shall beinvestigated before proceeding with the method (see Section11).6. Significance

46、and Use6.1 The health of workers in many industries, for example,mining, metal refining, battery manufacture, construction, etc.,is at risk through exposure by inhalation of particulate lead andlead compounds. Industrial hygienists and other public healthprofessionals need to determine the effective

47、ness of measurestaken to control workers exposure, and this is generallyachieved by making workplace air measurements. This stan-dard has been published in order to make available a methodfor making valid exposure measurements for lead. It will be ofbenefit to: agencies concerned with health and saf

48、ety at work;industrial hygienists and other public health professionals;analytical laboratories; industrial users of metals and metal-loids and their workers, etc. It has been assumed in the draftingof this standard that the execution of its provisions, and theinterpretation of the results obtained,

49、 is entrusted to appropri-ately qualified and experienced people.6.2 The measuring procedure shall comply with any rel-evant International, European or National Standard that speci-fies performance requirements for procedures for measuringchemical agents in workplace air (for example, EN 482).7. ReagentsNOTE 1During the analysis, use only reagents of recognized analyti-cal grade, and only water as specified in 7.1.7.1 Water, complying with the requirements for Specifica-tion D1193, grade 2 water (electrical conductivity l