Standard Test Method for Determination of 2,4-Toluene Di<emph type="bdit">iso</emph >cyanate (2,4-TDI) and 2,6-Toluene Di<emph type="bdit">iso</emph>cyanate (2,6-TDI) in Air (with 9-(N-Methylaminomethyl) Anthracene Method) (MAMA) in the Workplace

SIGNIFICANCE AND USE
5.1 TDI is used mostly in the preparation of rigid and semi-rigid foams and adhesives.  
5.2 Diisocyanates and polyisocyanates are irritants to skin, eyes, and mucous membranes. They are recognized to cause respiratory allergic sensitization, asthmatic bronchitis, and acute respiratory intoxication (6-9).  
5.3 The American Conference of Governmental Industrial Hygienists (ACGIH) has adopted a Threshold Limit Value–Time Weighted Average (TLV-TWA) of 0.001 ppm of 0.007 mg/m3 with a Short-Term Exposure Limit (STEL) of 0.005 ppm or 0.036 mg/m3 for either 2,4–TDI, or 2,6–TDI, or for a mixture of 2,4– and 2,6–TDI (10). The Occupational Safety and Health Administration of the U.S. Department of Labor (OSHA) has a permissible exposure limit of 0.02 ppm(V) or 0.14 mg/m3 of 2,4-TDI as a ceiling limit and 0.005 ppm (V) or 0.036 mg/m3 as a time-weighted average (11).  
5.4 Monitoring of respiratory and other problems related to diisocyanates and polyisocyanates is aided through the utilization of this test method, due to its sensitivity and low volume requirements (15 L). Its short sampling times are compatible with the duration of many industrial processes and its low quantification limit also suits the concentrations often found in the working area.  
5.5 The segregating sampling device pertaining to this proposed test method physically separates gas and aerosol allowing isocyanate concentrations in both physical states to be obtained, thus helping in the selection of ventilation systems and personal protection.  
5.6 This test method is used to measure gaseous concentrations of 2,4- and 2,6-TDI in air for workplace and ambient atmospheres.
SCOPE
1.1 This test method covers the determination of gaseous 2,4-toluene diisocyanate (2,4-TDI) and 2,6-toluene diisocyanate (2,6-TDI) in air samples collected from workplace and ambient atmospheres.  
1.2 Differential air sampling is performed with a segregating device.2 The gaseous fraction is collected on a glass fiber filter (GFF) impregnated with 9-(N-methylaminomethyl) anthracene (MAMA).  
1.3 The analysis of the gaseous fraction is performed with a high performance liquid chromatograph (HPLC) equipped with ultraviolet (UV) and fluorescence detectors. An ultra high performance liquid chromatograph (UPLC) can also be used, provided that its performance is equivalent to what is stated in this standard.  
1.4 The analysis of the aerosol fraction is performed separately as described in Ref (1).3  
1.5 The range of application of this test method, utilizing UV and a fluorescence detector, is validated for 0.014 to 1.16 μg of monomer 2,4- and 2,6-TDI/2.0 mL of desorption solution, which corresponds to concentrations of 0.001 to 0.077 mg/m3 of TDI based on a 15-L air sample. This corresponds to 0.0.14 to 11 ppb(V) and brackets the established TLV value of 1 ppb(v).  
1.6 A field blank sampling system is used to check the possibility of contamination during the entire sampling and analysis.  
1.7 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.  
1.8 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. See Section 9 for additional hazards.  
1.9 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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ASTM D5932-20 - Standard Test Method for Determination of 2,4-Toluene Di<emph type="bdit">iso</emph >cyanate (2,4-TDI) and 2,6-Toluene Di<emph type="bdit">iso</emph>cyanate (2,6-TDI) in Air (with 9-(N-Methylaminomethyl) Anthracene Method) (MAMA) in the Workplace
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REDLINE ASTM D5932-20 - Standard Test Method for Determination of 2,4-Toluene Di<emph type="bdit">iso</emph >cyanate (2,4-TDI) and 2,6-Toluene Di<emph type="bdit">iso</emph>cyanate (2,6-TDI) in Air (with 9-(N-Methylaminomethyl) Anthracene Method) (MAMA) in the Workplace
English language
7 pages
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This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the
Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
Designation: D5932 − 20
Standard Test Method for
Determination of 2,4-Toluene Diisocyanate (2,4-TDI) and 2,6-
Toluene Diisocyanate (2,6-TDI) in Air (with 9-(N-
Methylaminomethyl) Anthracene Method) (MAMA) in the
1
Workplace
This standard is issued under the fixed designation D5932; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope 1.7 The values stated in SI units are to be regarded as
standard. No other units of measurement are included in this
1.1 This test method covers the determination of gaseous
standard.
2,4-toluene diisocyanate (2,4-TDI) and 2,6-toluene diisocya-
1.8 This standard does not purport to address all of the
nate (2,6-TDI) in air samples collected from workplace and
ambient atmospheres. safety concerns, if any, associated with its use. It is the
responsibility of the user of this standard to establish appro-
1.2 Differential air sampling is performed with a segregat-
2
priate safety, health, and environmental practices and deter-
ing device. The gaseous fraction is collected on a glass fiber
mine the applicability of regulatory limitations prior to use.
filter (GFF) impregnated with 9-(N-methylaminomethyl) an-
See Section 9 for additional hazards.
thracene (MAMA).
1.9 This international standard was developed in accor-
1.3 The analysis of the gaseous fraction is performed with a
dance with internationally recognized principles on standard-
high performance liquid chromatograph (HPLC) equipped
ization established in the Decision on Principles for the
with ultraviolet (UV) and fluorescence detectors.An ultra high
Development of International Standards, Guides and Recom-
performance liquid chromatograph (UPLC) can also be used,
mendations issued by the World Trade Organization Technical
provided that its performance is equivalent to what is stated in
Barriers to Trade (TBT) Committee.
this standard.
2. Referenced Documents
1.4 The analysis of the aerosol fraction is performed sepa-
3
4
rately as described in Ref (1).
2.1 ASTM Standards:
D1193 Specification for Reagent Water
1.5 The range of application of this test method, utilizing
UV and a fluorescence detector, is validated for 0.014 to 1.16 D1356 Terminology Relating to Sampling and Analysis of
Atmospheres
µg of monomer 2,4- and 2,6-TDI/2.0 mL of desorption
solution, which corresponds to concentrations of 0.001 to D1357 Practice for Planning the Sampling of the Ambient
3
Atmosphere
0.077 mg/m of TDI based on a 15-L air sample. This
correspondsto0.0.14to11ppb(V)andbracketstheestablished D4840 Guide for Sample Chain-of-Custody Procedures
D5337 Practice for Flow RateAdjustment of Personal Sam-
TLV value of 1 ppb(v).
pling Pumps
1.6 A field blank sampling system is used to check the
2.2 Other Documents:
possibility of contamination during the entire sampling and
5
Sampling Guide for Air Contaminants in the Workplace
analysis.
3. Terminology
1
This test method is under the jurisdiction of ASTM Committee D22 on Air
Quality and is the direct responsibility of Subcommittee D22.04 on Workplace Air
3.1 For definitions of terms used in this test method, refer to
Quality.
Terminology D1356.
Current edition approved March 1, 2020. Published May 2020. Originally
ɛ1
approved in 1996. Last previous edition approved in 2013 as D5932 – 08 (2013) .
DOI: 10.1520/D5932-20.
2 4
ASTM International takes no position respecting the validity of any patent For referenced ASTM standards, visit the ASTM website, www.astm.org, or
rights asserted in connection with any item mentioned in this standard. Users of this contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
standard are expressly advised that determination of the validity of any such patent Standards volume information, refer to the standard’s Document Summary page on
rights, and the risk of infringement of such rights, are entirely their own the ASTM website.
5
responsibility. Available from Institut de Recherche en Santé et en Sécurité du Travail
3
The boldface numbers in parentheses refer to a list of references at the end of (IRSST), Laboratory Division, Montreal, QC, 2012, http://www.irsst.qc.ca/media/
this standard. documents/Pubirsst/T-15.pdf.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1

---------------------- Page: 1 ----------------------
D5932 − 20
4. Summary of Test Method with the duration of many industrial processes and its low
quanti
...

This document is not an ASTM standard and is intended only to provide the user of an ASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
´1
Designation: D5932 − 08 (Reapproved 2013) D5932 − 20
Standard Test Method for
Determination of 2,4-Toluene DiisocyanateDiisocyanate (2,4-
TDI) and 2,6-Toluene DiisocyanateDiisocyanate (2,6-TDI) in
Air (with 9-(N-Methylaminomethyl) Anthracene Method)
1
(MAMA) in the Workplace
This standard is issued under the fixed designation D5932; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1
ε NOTE—Editorial corrections were made to 8.14.8 and 11.2.1 in March 2015.
1. Scope
1.1 This test method covers the determination of gaseous 2,4-toluene diisocyanate (2,4-TDI) and 2,6-toluene diisocyanate
(2,6-TDI) in air samples collected from workplace and ambient atmospheres.
2,
1.2 Differential air sampling is performed with a segregating device. The gaseous fraction is collected on a glass fiber filter
(GFF) impregnated with 9-(N-methylaminomethyl) anthracene (MAMA).
1.3 The analysis of the gaseous fraction is performed with a high performance liquid chromatograph (HPLC) equipped with
ultraviolet (UV) and fluorescence detectors. An ultra high performance liquid chromatograph (UPLC) can also be used, provided
that its performance is equivalent to what is stated in this standard.
3
1.4 The analysis of the aerosol fraction is performed separately as described in Ref (1).
1.5 The range of application of this test method, utilizing UV and a fluorescence detector, is validated for 0.0290.014 to 1.16
μg of monomer 2,4- and 2,6-TDI/2.0 mL of desorption solution, which corresponds to concentrations of 0.0020.001 to 0.077
3
mg/m of TDI based on a 15-L air sample. This corresponds to 0.280.0.14 to 11 ppb(V) and brackets the established TLV value
of 51 ppb(v).
1.6 A field blank sampling system is used to check the possibility of contamination during the entire sampling and analysis.
1.7 The values stated in SI units are to be regarded as the standard. No other units of measurement are included in this standard.
1.8 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility
of the user of this standard to establish appropriate safety safety, health, and healthenvironmental practices and determine the
applicability of regulatory limitations prior to use. See Section 9 for additional hazards.
1.9 This international standard was developed in accordance with internationally recognized principles on standardization
established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued
by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
2. Referenced Documents
4
2.1 ASTM Standards:
D1193 Specification for Reagent Water
D1356 Terminology Relating to Sampling and Analysis of Atmospheres
D1357 Practice for Planning the Sampling of the Ambient Atmosphere
D4840 Guide for Sample Chain-of-Custody Procedures
1
This test method is under the jurisdiction of ASTM Committee D22 on Air Quality and is the direct responsibility of Subcommittee D22.04 on Workplace Air Quality.
Current edition approved April 1, 2013March 1, 2020. Published April 2013May 2020. Originally approved in 1996. Last previous edition approved in 20082013 as D5932
ɛ1
– 08. – 08 (2013) . DOI: 10.1520/D5932-08R13E01.10.1520/D5932-20.
2
The American Society for Testing and Materials ASTM International takes no position respecting the validity of any patent rights asserted in connection with any item
mentioned in this standard. Users of this standard are expressly advised that determination of the validity of any such patent rights, and the risk of infringement of such rights,
are entirely their own responsibility.
3
The boldface numbers in parentheses refer to thea list of references at the end of this test method.standard.
4
For referenced ASTM standards, visit the ASTM website, www.astm.org, or contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1

---------------------- Page: 1 ----------------------
D5932 − 20
D5337 Practice for Flow Rate Adjustment of Personal Sampling Pumps
2.2 Other Documents:
5
Sampling Guide for Air Conta
...

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