Literature DB >> 9075314

Air and biological monitoring of toluene diisocyanate in a flexible foam plant.

H Tinnerberg1, M Dalene, G Skarping.   

Abstract

Comparative air measurements of toluene diisocyanate (TDI) were performed in a 5.6 m3 standard atmosphere and at a TDI flexible foam plant. Air samples were collected in midget impinger flasks containing 9-(N-methyl-amino-methyl)-anthracene (MAMA) in toluene and on 13-mm glass-fiber filters impregnated with MAMA and glycerol analyzed by LC-UV and with filter-tape instruments. In the laboratory study the average amounts of the TDI-MAMA derivatives determined were higher for filters compared to impingers when tested at concentrations between 16 and 150 micrograms/m3 (n = 29). At the TDI foaming plant the amount of TDI-MAMA collected on the filters compared with impingers showed higher TDI values at low concentrations and lower values at higher concentrations. The same was seen for the filter-tape measurements, but for two samples at very low concentrations the response was much lower. The average air concentration was 29.8 micrograms/m3 (12.5-79.9; n = 12). The highest exposure peak measured was approximately 3 mg TDI/m3. 2,4- and 2,6-toluene diamine (TDA) in urine (U-TDA) and in plasma (P-TDA) from four exposed workers and one volunteer were determined after strong acid hydrolysis as their pentafluoro-propionic anhydride derivatives using gas chromatography-mass spectrometry. The ions monitored were the M-20 ions (M = molecular weight) of the TDA and trideuterium labeled TDA as the internal standard. The P-TDA among the workers varied between 1-38 micrograms/L and between 7-24 micrograms/L for 2,4- and 2,6-TDA, respectively. The individual plasma levels among the workers over the 3-day periods varied between 7-73%. For the volunteer, P-TDA reached a maximum about 24 hours after the last exposure. The half-time of P-TDA for the volunteer was about 10 days. The urine levels (U-TDA) varied greatly with time and exposure. High peaks were found during or shortly after the exposure. No clear correlation between air levels of TDI measured with the filter-tape instruments and levels of TDA in hydrolyzed urine and plasma was seen, but the U-TDAMax followed the exposure in time as measured with the filter-tape instruments.

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Year:  1997        PMID: 9075314     DOI: 10.1080/15428119791012883

Source DB:  PubMed          Journal:  Am Ind Hyg Assoc J        ISSN: 0002-8894


  4 in total

1.  Dermal, inhalation, and internal exposure to 1,6-HDI and its oligomers in car body repair shop workers and industrial spray painters.

Authors:  A Pronk; F Yu; J Vlaanderen; E Tielemans; L Preller; I Bobeldijk; J A Deddens; U Latza; X Baur; D Heederik
Journal:  Occup Environ Med       Date:  2006-05-25       Impact factor: 4.402

2.  Diagnosis and prevention of diseases induced by isocyanate.

Authors:  Kazuko Nakashima; Tatsuya Takeshita; Kanehisa Morimoto
Journal:  Environ Health Prev Med       Date:  2002-05       Impact factor: 3.674

3.  Improvement in the GC-MS method for determining urinary toluene-diamine and its application to the biological monitoring of workers exposed to toluene-diisocyanate.

Authors:  Tadashi Sakai; Yoko Morita; Jaehoon Roh; Hyoungryoul Kim; Yangho Kim
Journal:  Int Arch Occup Environ Health       Date:  2005-05-26       Impact factor: 3.015

4.  Antibodies to toluene diisocyanate in an environmentally exposed population.

Authors:  K G Orloff; D Batts-Osborne; T Kilgus; S Metcalf; M Cooper
Journal:  Environ Health Perspect       Date:  1998-10       Impact factor: 9.031

  4 in total

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