ASTM D6561-2006(2016) 2147 Standard Test Method for Determination of Aerosol Monomeric and Oligomeric Hexamethylene Diisocyanate (HDl) in Air with (Methoxy-2&x2013 phenyl-1) Pipera.pdf

1、Designation: D6561 06 (Reapproved 2016)Standard Test Method forDetermination of Aerosol Monomeric and OligomericHexamethylene Diisocyanate (HDl) in Air with (Methoxy-2phenyl-1) Piperazine (MOPIP) in the Workplace1This standard is issued under the fixed designation D6561; the number immediately follo

2、wing the designation 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.1. Scope1.1 This test method

3、covers the determination of aerosolhexamethylene diisocyanate (HDI) in air samples collectedfrom workplace and ambient atmospheres. The method de-scribed in this test method collects separate fractions. Onefraction will be dominated by vapor, and the other fraction willbe dominated by aerosol. It is

4、 not known at the present timewhether this represents a perfect separation of vapor andaerosol, and in any case, there are not separate exposurestandards for vapor and aerosol. Therefore, in comparing theresults for isocyanate against a standard, results from the twofractions should be combined to g

5、ive a single total value. Thereason for splitting the sample into two fractions is to increaseanalytic sensitivity for the vapor fraction and also to give thehygienist or ventilation engineer some information concerningthe likely state of the isocyanate species. The analyses of thetwo fractions are

6、different, and are provided in separate, linked,standards to avoid confusion. This test method is principallyused to determine short term exposure (15 min) of HDI inworkplace environments for personal monitoring or in ambientair. The analysis of the vapor fraction is performed separately,as describe

7、d in Test Method D6562.1.2 Differential air sampling is performed with a segregat-ing device.2The aerosol fraction is collected on a polytetra-fluoroethylene (PTFE) filter.1.3 Immediately after sampling, the PTFE filter is trans-ferred into a jar containing a (methoxy-2 phenyl-1) piperazine(MOPIP) s

8、olution in toluene.1.4 The analysis of the aerosol fraction is performed byusing a high performance liquid chromatograph (HPLC)equipped with an ultraviolet (UV) detector. The range ofapplication of the test method has been validated from 0.052 to1.04 g of monomeric HDI/mL, which corresponds, based o

9、na 15 Lair sample, to concentrations from 0.004 to 0.070 mg/m3of HDI. Those concentrations correspond to a range of aerosolphase concentrations from 0.5 ppb (V) to 10 ppb (V) and coverthe established threshold limit valve (TLV) value of 5 ppb (V).1.5 The quantification limit for the monomeric HDI is

10、 0.041g per mL, which corresponds to 0.003 mg/m3fora15Lsampled air volume. This value is equivalent to ten times thestandard deviation obtained from ten measurements carried outon a standard solution in contact with the PTFE filter whoseconcentration of 0.1 g/mL is close to the expected detectionlim

11、it.1.6 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.7 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 a

12、ppro-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use. See Section 9 foradditional hazards.2. Referenced Documents2.1 ASTM Standards:3D1193 Specification for Reagent WaterD1356 Terminology Relating to Sampling and Analysis ofAtmospheresD1357

13、Practice for Planning the Sampling of the AmbientAtmosphereD5337 Practice for Flow Rate Adjustment of Personal Sam-pling Pumps1This test method is under the jurisdiction of ASTM Committee D22 on AirQuality and is the direct responsibility of Subcommittee D22.04 on Workplace AirQuality.Current editio

14、n approved Nov. 1, 2016. Published November 2016. Originallyapproved in 2000. Last previous edition approved in 2011 as D6561 06 (2011).DOI: 10.1520/D6561-06R16.2The sampling device for isocyanates is covered by a patent held by JacquesLesage et al, IRSST, 505 De Maisonneuve Blvd. West, Montreal, Qu

15、ebec, Canada.If you are aware of an alternative to this patented item, please provide thisinformation to ASTM Headquarters. Your comments will receive careful consider-ation at a meeting of the responsible technical committee,1which you may attend.3For referenced ASTM standards, visit the ASTM websi

16、te, 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.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States

17、1D6562 Test Method for Determination of Gaseous Hexam-ethylene Diisocyanate (HDI) in Air with 9-(N-methylaminomethyl) Anthracene Method (MAMA) in theWorkplace2.2 Other Standard:4Sampling Guide for Air Contaminants in the Workplace3. Terminology3.1 Definitions:3.1.1 For definitions of terms used in t

18、his test method, referto Terminology D1356.4. Summary of Test Method4.1 Vapor and aerosol fractions are sampled simultaneouslyby using a segregating sampling device. The aerosols arecollected on PTFE filter while the gaseous fraction is beingadsorbed on a second filter made of glass fiber, impregnat

19、edwith a 9-(N-methylaminomethyl) anthracene (MAMA).4.2 The analysis of the monomer in the gaseous fraction isperformed separately in accordance with the procedure de-scribed in Test Method D6562.4.3 Diisocyanates present as aerosols are collected on thePTFE filter and derivatized in a MOPIP solution

20、 (1, 2).5SeeFig. 1.4.3.1 The solution is then evaporated to dryness andredissolved, using the acetic anhydride solution (see 8.11).Monomeric and oligomeric HDI are separated by using areversed phase HPLC column, and detection is made by usingan HPLC equipped with UV detection.4.4 Concentration of mo

21、nomeric and oligomeric diisocya-nates contained in a sample is calculated by using an externalstandard of the monomeric HDI.5. Significance and Use5.1 HDI is mostly used in the preparation of paints. For thelast ten years, the use of isocyanates and their industrial needshave been in constant growth

22、.5.2 Diisocyanates and polyisocyanates are irritants to skin,eyes, and mucous membranes. They are recognized to causerespiratory allergic sensitization, asthmatic bronchitis, andacute respiratory intoxication (3-6).5.3 The American Conference of Governmental IndustrialHygienists (ACGIH) has adopted

23、a threshold limit value - timeweighted average (TLV TWA) of 0.005 ppm (V) or 0.034mg/m3for monomeric HDI (7). The Occupational Safety dual filter sampling system; hexameth-ylene diisocyanate; high-performance liquid chromatography;(methoxy-2phenyl-1) piperazine; sampling and analysis;workplace atmos

24、pheresREFERENCES(1) Lesage, J., and Perrault, G., “A Charactrisation Charactrisationphysique et chimique de lexposition des travailleurs auxisocyanates,” Rapport de recherche, Institut de recherche en sant eten scurit du travail du Qubec, 1989, Montral, Qubec.(2) Lesage, J., Goyer, N., Desjardins, F

25、., Vincent, J.-Y., and Perrault, G.,“WorkersExposure to Isocyanates” American Industrial HygieneAssociation Journal, Vol 53, No. 2, 1992, pp. 146153.(3) A Criteria for a Recommended Standard “Occupational Exposure toToluene Diisocyanate,” Department of Health, Education andWelfare, National Institut

26、e for Occupational Safety and Health,Cincinnati, OH, No. DHEW (NIOSH) 73-11022, 1973.(4) Woolrich, P.F.,“Toxicology, Industrial Hygiene and Medical Controlof TDI, MDI and PMPPI,” American Industrial Hygiene AssociationJournal, Vol 43, 1981, pp. 8997.(5) Moller, D. R., et al, “Chronic Asthma Due to T

27、oluene Diisocyanate,”Chest, Vol 90, No. 4, 1986, pp. 494499.(6) Butcher, B. T., et al, “Polyisocyanates and Their Prepolymers,”Asthma in the Workplace, Chap. 20, edited by I. Leonard Bernstein,Moira Chan-Yeung, Jean-Luc Malo, and David I. Bernstein,Cincinnati, Ohio, 1994, pp. 415436.(7) Threshold Li

28、mit Values for Chemical Substances and Physical Agentsand Biological Exposure Indices, ACGIH, Cincinnati, Ohio, 1993.(8) Occupational Safety and Health Administration (OSHA): OSHAMethod 42: Diisocyanates, OSHA Analytical Laboratory, OrganicMethods Development Branch, Salt Lake City, Utah, 1989.(9) L

29、esage, J., and Perrault, G., “Sampling Device for Isocyanates,” U.S.Patent No. 4 961 916.(10) Occupational Safety and Health Administration (OSHA): Evaluationscheme methods that use filters as the collection medium, OSHATechnical Center, OSHAAnalytical Methods Manuals, 2nd Ed., Part2, Salt Lake City

30、, Utah, 1991.(11) Guide dchantillonnage des contaminants de lair en milieu detravail, Institut de recherche en sant et en scurit du travail duQubec, Montral, 1999.FIG. 2 Means of the Z-Scores Obtained by Ten Laboratories After n $ 3 Participations to an Interlaboratory EvaluationTest MethodD6561D656

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