Brorson T, Skarping G, Renman L, Sangö C
Department of Occupational and Environmental Medicine, University Hospital, Lund, Sweden.
Int Arch Occup Environ Health. 1989;61(8):495-501. doi: 10.1007/BF00683118.
An all glass apparatus for the generation of air concentrations of 2,4-toluene diisocyanate (2,4-TDI), 2,6-toluene diisocyanate (2,6-TDI) and 1,6-hexamethylene diisocyanate (HDI) was developed. The generation principle was based on gas-phase permeation with permeation membranes of silicon rubber. In an 8 m3 stainless steel test chamber, low and steady TDI-and HDI atmospheres (1-100 micrograms/m3) could be maintained. The diisocyanate concentrations were determined by an HPLC method, using the 9-(N-methylaminomethyl)-anthracene reagent utilizing UV detection. The sum of diisocyanates and their related amines were determined by sampling in 0.4 M hydrochloric acid solution, and analysis by capillary gas chromatography with thermionic specific detection. Related amines were determined by sampling in ethanol - 0.2% KOH and analysis on GC-TSD. A continuous band-tape monitor was used for the determination of diisocyanates. Losses of diisocyanates in the test chamber were evaluated by measuring the TDI and HDI concentrations at the inlet respectively the outlet of the test chamber. At the outlet of the test chamber, ca 25% of the TDI respectively HDI concentrations were recovered. With a male subject in the test chamber ca 15% of the HDI concentration was recovered. The air flow through the test chamber was ca 10 m3/h. The changes in isomeric composition of airborne TDI, at stopped flow conditions, showed that the decay of the 2,4-isomer was faster than of the 2,6-isomer. No trace of the related amine toluene diamine (TDA) was detected in the test chamber, at TDI concentrations ranging from 20 to 50 micrograms/m3. Sampling losses due to sampling connections were evaluated.(ABSTRACT TRUNCATED AT 250 WORDS)
开发了一种用于生成空气中2,4-甲苯二异氰酸酯(2,4-TDI)、2,6-甲苯二异氰酸酯(2,6-TDI)和1,6-六亚甲基二异氰酸酯(HDI)浓度的全玻璃装置。生成原理基于用硅橡胶渗透膜进行气相渗透。在一个8立方米的不锈钢测试舱中,可以维持低且稳定的TDI和HDI气氛(1 - 100微克/立方米)。二异氰酸酯浓度通过高效液相色谱法测定,使用9 -(N - 甲基氨基甲基)-蒽试剂并利用紫外检测。二异氰酸酯及其相关胺类的总和通过在0.4 M盐酸溶液中采样并通过带有热离子特定检测的毛细管气相色谱分析来测定。相关胺类通过在乙醇 - 0.2%氢氧化钾中采样并在气相色谱 - 热离子特定检测上进行分析来测定。使用连续带状监测器测定二异氰酸酯。通过分别测量测试舱入口和出口处的TDI和HDI浓度来评估测试舱中二异氰酸酯的损失。在测试舱出口处,分别回收了约25%的TDI和HDI浓度。测试舱中有一名男性受试者时,回收了约15%的HDI浓度。通过测试舱的气流约为10立方米/小时。在停止流动条件下,空气中TDI异构体组成的变化表明,2,4 - 异构体的衰减比2,6 - 异构体快。在测试舱中,当TDI浓度范围为20至50微克/立方米时,未检测到相关胺甲苯二胺(TDA)的痕迹。评估了由于采样连接导致的采样损失。(摘要截断于250字)