Page:NIOSH Manual of Analytical Methods - 5516.pdf/1
5516
2,4- and 2,6-TOLUENEDIAMINE
(in the presence of isocyanates)
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CH3C6H3(NH2)2 |
MW: 122.17 |
CAS: 2,4-: 95-80-7 CAS: 2,6-: 823-40-5 |
RTECS: 2,4-: XS9625000 RTECS: 2,6-: XS9750000 |
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METHOD: 5516, Issue 2 |
EVALUATION: PARTIAL |
Issue 1: 15 May 1989 Issue 2: 15 August 1994 |
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OSHA: no PEL NIOSH: 2,4-: lowest feasible; carcinogen ACGIH: no TLV
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PROPERTIES: 2,4-: solid; MP 99 °C 2,6-: solid; MP 106 °C |
SYNONYMS: 2,4-: 4-methyl-1,3-benzenediamine; 2,4-diaminotoluene
2,6-: 2-methyl-1,3-benzenediamine; 2,6-diaminotoluene
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SAMPLING |
MEASUREMENT |
ACCURACY
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APPLICABILITY: The working range is 3 to 30 μg/m3 for a 100-L air sample. This method, based on that of Warwick et al. for isocyanates [2], determines 2,4- and 2,6-toluenediamine in air in the presence of isocyanates. Samples from polyurethane foam plants were analyzed simultaneously for 2,4- and 2,6-toluenediamine and 2,4- and 2,6-toluene diisocyanate [1].
INTERFERENCES: m-Phenylenediamine interferes in the determination of 2,4-toluenediamine.
OTHER METHODS: Holdren et al. [3] reported a similar method using N-(4-nitrobenzyl)propylamine in toluene for sampling and HPLC with electrochemical detection. Other methods are: (a) absorb on Tenax GC, desorb in toluene, GC [4]; (b) absorb on silica gel, desorb in 2-butanone, GC [5]; (c) sample in aqueous acid, work up, GC of free amines [6] or bis(heptafluoro butyryl)amides [7,8]; (d) sample in ethanolic KOH, workup, LC of free amine [9,10] or GC of bis(pentafluoropropionyl) amides [11]; (e) sample with sulfuric acid-coated filter, work up, GC of bis(heptafluorobutyryl)amides [12]. Some of these methods [3,9—11] can be used for the simultaneous determination of toluenediamines and toluene diisocyanates.
NIOSH Manual of Analytical Methods (NMAM), Fourth Edition