ASTM D5836-2008(2013) 6250 Standard Test Method for Determination of 2 4-Toluene Diisocyanate (2 4-TDI) and 2 6-Toluene Diisocyanate (2 6-TDI) in Workplace Atmospheres (1-2 PP Meth.pdf

《ASTM D5836-2008(2013) 6250 Standard Test Method for Determination of 2 4-Toluene Diisocyanate (2 4-TDI) and 2 6-Toluene Diisocyanate (2 6-TDI) in Workplace Atmospheres (1-2 PP Meth.pdf》由会员分享，可在线阅读，更多相关《ASTM D5836-2008(2013) 6250 Standard Test Method for Determination of 2 4-Toluene Diisocyanate (2 4-TDI) and 2 6-Toluene Diisocyanate (2 6-TDI) in Workplace Atmospheres (1-2 PP Meth.pdf（5页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D5836 08 (Reapproved 2013)Standard Test Method forDetermination of 2,4-Toluene Diisocyanate (2,4-TDI) and 2,6-Toluene Diisocyanate (2,6-TDI) in Workplace Atmospheres(1-2 PP Method)1This standard is issued under the fixed designation D5836; the number immediately following the designatio

2、n 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 describes the deter

3、mination of 2,4-toluene diisocyanate (2,4-TDI) and 2,6-toluene diisocyanate(2,6-TDI) in air samples collected from workplace atmo-spheres in a cassette containing a glass-fiber filter impregnatedwith 1-(2-pyridyl)piperazine (1-2 PP). This procedure is veryeffective for determining the vapor content

4、of atmospheres.Atmospheres containing aerosols may cause TDI results to beunderestimated.1.2 This test method uses a high-performance liquid chro-matograph (HPLC) equipped with a fluorescence or an ultra-violet (UV) detector (1-4).2,31.3 The validated range of the test method, as written, isfrom 1.4

5、 to 5.6 g of 2,4-TDI and 2,6-TDI which is equivalentto approximately 9.8 to 39 ppb for 2,4-TDI and 2,6-TDI basedon a 20-L air sample. The HPLC method using an UV detectoris capable of detecting 0.078 g of 2,4-TDI and 0.068 g of2,6-TDI in a 4.0-mL solvent volume, which is equivalent to0.55 ppb for 2,

6、4-TDI and 0.48 ppb for 2,6-TDI based on a 20-Lair sample.1.4 The isomers of 2,4-TDI, and 2,6-TDI, can be separatedutilizing a reversed phase column for the HPLC method.Because industrial applications employ an isomeric mixture of2,4- and 2,6-TDI, the ability to achieve this separation isimportant.1.

7、5 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.6 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-

8、priate safety and health practices and determine the applica-bility of regulatory limitations prior to use. See Section 9 forspecific precautions.2. Referenced Documents2.1 ASTM Standards:4D1193 Specification for Reagent WaterD1356 Terminology Relating to Sampling and Analysis ofAtmospheresD1357 Pra

9、ctice for Planning the Sampling of the AmbientAtmosphereD3686 Practice for Sampling Atmospheres to Collect Or-ganic Compound Vapors (Activated Charcoal Tube Ad-sorption Method)E691 Practice for Conducting an Interlaboratory Study toDetermine the Precision of a Test Method3. Terminology3.1 For defini

10、tions of terms used in this test method, refer toTerminology D1356.4. Summary of Test Method4.1 A known volume of air is drawn through a cassettecontaining a glass-fiber filter impregnated with 1-(2-pyridyl)piperazine. The diisocyanate reacts with the secondaryamine to form a urea derivative.4.2 The

11、 coated glass-fiber filter is extracted with acetonitrile(ACN) containing 10 % dimethyl sulfoxide (DMSO) and theextract is analyzed by HPLC. The eluent is monitored with afluorescence detector (240-nm excitation, 370-nm emissioncutoff filter) or a UV detector (254 nm).1This test method is under the

12、jurisdiction of ASTM Committee D22 on AirQuality and is the direct responsibility of Subcommittee D22.04 on Workplace AirQuality.Current edition approved April 1, 2013. Published April 2013. Originallyapproved in 1995. Last previous edition approved in 2008 as D5836 - 08. DOI:10.1520/D5836-08R13.2Va

13、lidation data and a preliminary draft of this test method were provided by theSalt Lake Technical Center of the U.S. Dept. of Labor, Occupational Safety andHealth Administration, Salt Lake City, UT.3The boldface numbers in parentheses refer to the references at the end of thistest method.4For refere

14、nced 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.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West C

15、onshohocken, PA 19428-2959. United States14.3 The amount of the urea derivative collected is deter-mined by comparison of sample response (peak area integra-tions or peak heights) to a standard calibration curve for theurea derivative.4.4 The amount of diisocyanate is calculated from theamount of ur

16、ea determined in the analysis.5. Significance and Use5.1 Diisocyanates are used in the production of polyure-thane foams, plastics, elastomers, surface coatings, and adhe-sives (5,6). It has been estimated that the production of TDIwill steadily increase during the future years.5.2 Diisocyanates are

17、 irritants to eyes, skin, and mucousmembrane and are respiratory sensitizers. Chronic exposure tolow concentrations of diisocyanates produces an allergic sen-sitization which may progress into asthmatic bronchitis (7,8).5.3 The Occupational Safety and Health Administration(OSHA) has a permissible ex

18、posure limit (PEL) for 2,4-TDI of0.02 ppm or 0.14 mg/m3as a ceiling limit. There is no OSHAPELfor 2,6TDI(9). TheAmerican Conference of Governmen-tal Industrial Hygienists (ACGIH) has a timeweighted aver-age (TWA) Threshold Limit Value (TLV) of 0.005 ppm or0.036 mg/m3and a short-term exposure limit (

19、STEL) of 0.02ppm or 0.14 mg/m3for either 2,4TDI, or 2,6TDI, or for amixture of 2,4 and 2,6TDI(10).5.4 This proposed test method has been found satisfactoryfor measuring 2,4 and 2,6-TDI levels in the workplace.6. Interferences6.1 Any compound having the same retention time as thestandards is a possib

20、le interference. Generally, chromato-graphic conditions can be altered to resolve an interference.6.2 Compounds that can react with an isocyanate representa potential interference. These would include molecules con-taining the functional groups: amines, alcohols, anhydrides,phenols, and carboxylic a

21、cids.6.3 Strong oxidizing agents can potentially react with the1-(2-pyridyl)piperazine.6.4 Retention time data on a single column is not definitiveproof of chemical identity. Analysis by an alternate columnsystem, ratioing of wavelength response using two wave-lengths or types of detector, should be

22、 performed to confirmchemical identity.7. Apparatus7.1 Sampling Equipment:7.1.1 Personal Sampling Pumps, any pump capable ofsampling at a rate of about 1.0 L/min for 8 h.7.1.2 Glass-Fiber Filters, 37 mm, free of organic binder,impregnated with 1.0 mg of 1-(2-pyridyl)piperazine.5,67.1.3 Cassette, pla

23、stic holders of the three-piece personalmonitor type, that accept filters of 37-mm diameter. Numberthe cassette for identification.7.1.4 Cellulose Backup Pad, sized to fit the cassette (7.1.3).7.2 Analytical Equipment:7.2.1 Liquid Chromatograph, a high-performance liquidchromatograph (HPLC) equipped

24、 with a fluorescence detectorcapable of monitoring 240-nm excitation and 370-nm cutoff ora UV detector capable of monitoring 254-nm wavelength anda manual or automatic sample injector.7.2.2 Liquid Chromatographic Column, an HPLC stainlesssteel column capable of separating the urea derivatives. Ana-l

25、ytical columns recommended in this test method are thefollowing: a 25-cm by 4.6-mm inside diameter stainless steelcolumn packed with 10-m Alltech C87; 6-m Zorbax CN8;5-m Zorbax TMS; 5-m Chromegabond TMS9; 5-m Spher-isorb C610; 5-m Supelcosil LC-CN11; or an equivalent col-umn.7.2.3 Electronic Integra

26、tor, an electronic integrator or someother suitable method of determining peak areas or heights.7.2.4 Pipets and Volumetrics, various sizes of volumetricpipets and flasks to prepare standards.7.2.5 Vials, glass vials with a 4-mL volume and fitted withpolytetrafluoroethylene-lined caps used for extra

27、ction ofsamples.8. Reagents and Materials8.1 Purity of ReagentsReagent grade chemicals shall beused in all tests. It is intended that all reagents shall conform tothe specifications of the Committees on Analytical Reagents ofthe American Chemical Society, where such specifications areavailable.12Oth

28、er grades may be used provided it can bedemonstrated that they are of sufficiently high purity to permittheir use without decreasing the accuracy of the determination.8.2 Purity of WaterUnless otherwise indicated, referencewater shall be understood to mean Type II reagent waterconforming to Specific

29、ation D1193, HPLC grade.8.3 Acetonitrile (CH3CN) HPLC grade.8.4 Ammonium Acetate(CH3COONH4)HPLC grade.8.5 Dimethyl Sulfoxide(CH3)2SO)HPLC grade.8.6 Extracting SolutionA solvent mixture of acetonitrileand dimethyl sulfoxide in the percentage of 90 and 10 (v/v),respectively.5ORBO-80 filters supplied b

30、y Supelco, Inc., Bellefonte, PA have been foundsatisfactory for this purpose.6Isocyanate glass fiber filters supplied by Forest Biomedical, Salt Lake City, UT,have been found satisfactory for this purpose.710-m ALLTECH C8 supplied by Alltech Associates, Deerfield, IL, has beenfound satisfactory for

31、this purpose.86-m ZORBAX CN and 5-m ZORBAX TMS supplied by E.I. DuPont,Wilmington, DE, have been found satisfactory for this purpose.95-m Chromegabond TMS supplied by ES Industries, Marlton, NJ, has beenfound satisfactory for this purpose.105-m Spherisorb C6 supplied by PhaseSep, Hauppauge, NY, has

32、been foundsatisfactory for this purpose.115-m Supelcosil LC-CN supplied by Supelco, Inc., Belleforte, PA has beenfound satisfactory for this purpose.12Reagent Chemicals, American Chemical Society Specifications , AmericanChemical Society, Washington, DC. For suggestions on the testing of reagents no

33、tlisted 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), Rockville,MD.D5836 08 (2013)28.7 Glacial Acetic Acid (CH3COOH)Reagent grade.8.8

34、 Hexane (C6H14)HPLC grade.8.9 Methylene Chloride(CH2Cl2)HPLC grade.8.10 Mobile PhaseA solvent mixture of acetonitrile (8.3)and water in the percentage of 37.5 and 62.5 (v/v), respectively.Add to the mobile phase enough ammonium acetate (8.4) (1.54to 7.7 g/L of solution or 0.02 to 0.1 N) to optimize

35、thechromatographic resolution. Add acetic acid (8.7)tothemixture to lower the pH to 6.0 to 6.2.8.11 1-(2-Pyridyl)piperazine (1-2 PP) (C9H13N3)Reagentgrade.138.12 N,N-(4-Methyl-1,3-phenylene)bis 4-(2-pyridinyl)-1-piperazinecarboxamide (C27H32N8O2)(2,4-TDIP).148.13 N,N-(2-Methyl-1,3-phenylene)bis 4-(2

36、-pyridinyl)-1-piperazinecarboxamide (C27H32N8O2)(2,6-TDIP).158.14 2,4-Toluene Diisocyanate (C9H6N2O2)Reagentgrade.168.15 2,6-Toluene Diisocyanate (C9H6N2O2)Reagentgrade.179. Safety Precautions9.1 The diisocyanates are potentially hazardous chemicalsand are extremely reactive. Avoid exposure to the d

37、iisocyanatestandards. Sample and standard preparations should be done inan efficient operating hood.9.2 Avoid skin contact with all solvents.9.3 Wear safety glasses at all times and other laboratoryprotective equipment as necessary.10. Sampling10.1 Refer to Practices D1357 and D3686 for generalinfor

38、mation on sampling.10.2 Equip the worker, whose exposure is to be evaluated,with a filter holder connected to a belt-supported samplingpump. Collect personal samples by pointing the samplerdownward in the breathing zone of the worker and remove thetop for open-face sampling. Draw air through the fil

39、ter at acalibrated rate of approximately 1.0 L/min and collect amaximum air sample of 15 L. Use a tripod or other support tolocate the sampler in the general room area for stationarymonitoring.10.3 Treat field blanks in the same manner as samples. Openthem in the environment to be sampled and immedi

40、ately closeand place with the samples to be sent to the laboratory foranalysis. Provide an unopened, unused cassette assembly as alaboratory blank. Submit at least one laboratory blank and onefield blank with each set of samples.11. Preparation of Apparatus11.1 Glass-Fiber FilterPrepare a fresh solu

41、tion of 2mg/mL of 1-(2-pyridyl)piperazine (8.11) in methylene chlorideevery time a batch of filters is to be coated. In an exhaust hood,set several glass-fiber filters on an appropriate holder, one thatwill support and not contaminate the filters. Using a pipet thatwill deliver 0.5 mL, place 0.5 mL

42、in the center of each filter.The liquid will just wet the filter; allow the filters to air-dry inthe hood for several minutes. Place the filters in a jar that islarge enough for the filters to lie flat. Place the jar in anunheated vacuum oven for 1 h (about 20-in. Hg vacuum) toremove residual methyl

43、ene chloride. Install the top on the jarand store in a refrigerator until ready for use. Coated filtersmay be stored for up to six months if they are stored in smallsealed jars in a refrigerator (4C). The filters should not bestored at ambient temperature for more a day or two.11.2 CassetteAssemble

44、the three-piece cassette, insertingthe cellulose backup pad into the bottom, adding an impreg-nated filter, and installing the ring and top. Seal the assemblyagainst air leakage by a wrap of masking tape or celluloseshrink bands, covering the crevice between the ring andbottom. Close the inlet and o

45、utlet openings of the cassette withplastic plugs.12. Calibration and Standardization12.1 Sample Pump CalibrationCalibrate the personalsampling pumps in accordance with Practice D3686,attherecommended flow rate with an assembled cassette betweenthe pump and the flow-measuring device. Calibrate the pu

46、mpbefore and after the sampling. If the postcalibration flow ratevaries more than 65 % from the precalibration flow rate,invalidate the sample.12.2 Standardization:12.2.1 Prepare a stock standard solution as micrograms ofTDIP per millilitre of dimethyl sulfoxide. Express the TDIP asthe free TDI. Mul

47、tiply the amount of TDIP by the correctionfactor derived from the ratios of the respective molecularweights of the TDI and TDIP. The factor is 0.3479 for TDI.12.2.2 Prepare working standards by diluting the stockstandard with acetonitrile.12.2.3 Prepare dilution standards at the necessary concen-tra

48、tions by diluting working standards with acetonitrile togenerate a full calibration curve that brackets the sampleconcentrations.12.2.4 Analyze by high-performance liquid chromatogra-phy using a suitable column and the mobile phase as describedin 8.10. The typical operating conditions are as follows

49、:Column temperature 25CFlow rate 1.0 mL/minUltraviolet 254 nmFluorescence 240 nm, excitation370 nm or none, emissioncutoff filterInjection size 525 LAnalytical conditions serve as a guideline and may need tobe modified depending upon the specific samples, columncondition, detector, and other parameters.131-(2-Pyridyl)piperazine supplied by Aldrich Chemical, Milwaukee, WI, hasbeen found satisfactory for this purpose.142,4-TDIP supplied by Supelco, Inc., Bellefonte, PA, is used for standardizationpurposes only.152,6-TDIP supplied by Supe