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一家软质泡沫塑料厂中甲苯二异氰酸酯的空气及生物监测

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

作者信息

Tinnerberg H, Dalene M, Skarping G

机构信息

Department of Occupational and Environmental Medicine, University Hospital, Lund, Sweden.

出版信息

Am Ind Hyg Assoc J. 1997 Mar;58(3):229-35. doi: 10.1080/15428119791012883.

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.

摘要

在5.6立方米的标准大气环境以及一家甲苯二异氰酸酯(TDI)软质泡沫工厂中,对TDI进行了空气对比测量。空气样本采集于装有甲苯中9-(N-甲基-氨基甲基)-蒽(MAMA)的小型冲击式吸收瓶中,以及浸渍有MAMA和甘油的13毫米玻璃纤维滤膜上,通过液相色谱-紫外检测法以及滤带式仪器进行分析。在实验室研究中,当在16至150微克/立方米的浓度范围内进行测试时(n = 29),与冲击式吸收瓶相比,滤膜上测定的TDI-MAMA衍生物平均含量更高。在TDI发泡工厂,与冲击式吸收瓶相比,滤膜上收集的TDI-MAMA在低浓度时TDI值较高,而在高浓度时较低。滤带式测量结果也是如此,但在两个低浓度样本中,响应值要低得多。平均空气浓度为29.8微克/立方米(12.5 - 79.9;n = 12)。测得的最高暴露峰值约为3毫克TDI/立方米。对4名暴露工人和1名志愿者的尿液(U-TDA)和血浆(P-TDA)中的2,4-和2,6-甲苯二胺(TDA),在强酸水解后,作为其五氟丙酸酐衍生物,使用气相色谱-质谱法进行测定。监测的离子是TDA的M - 20离子(M =分子量)以及作为内标的氘代TDA。工人中的P-TDA,2,4-TDA和2,6-TDA分别在1 - 38微克/升和7 - 24微克/升之间变化。在3天时间内,工人个体的血浆水平在7% - 73%之间变化。对于志愿者,P-TDA在最后一次暴露后约24小时达到最大值。志愿者的P-TDA半衰期约为10天。尿液水平(U-TDA)随时间和暴露情况变化很大。在暴露期间或暴露后不久会出现高峰值。用滤带式仪器测得的空气中TDI水平与水解尿液和血浆中TDA水平之间未发现明显相关性,但U-TDAMax随滤带式仪器测量的暴露情况而变化。

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