ASTM D5932-96(2002) PDF

SIGNIFICANCE AND USE TDI is used mostly in the preparation of rigid and semi-rigid foams and adhesives. Iso—cyanate use has been growing for the last ten years and the industrial need is still growing. 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 (Refs 6-9). The American Conference of Governmental Industrial Hygienists (ACGIH) has adopted a Threshold Limit Value–Time Weighted Average (TLV—TWA) of 0.036 mg/m3 with a Short-Term Exposure Limit (STEL) of 0.14 mg/m3 for 2,4-TDI (Ref 10). (Ref. ACGIH 1993–4). 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 TDI as a ceiling limit (11). 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 detection limit also suits the concentrations often found in the working area. 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. This test method is used to measure 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., 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. 1.4 The analysis of the aerosol fraction is performed separately as described in Ref (). 1.5 The range of application of this test method, utilizing UV and a fluorescence detector, is validated for 0.02 to 4.2 g of monomer 2,4- and 2,6-TDI/2.0 mL of desorption solution, which corresponds to concentrations of 0.001 to 0.28 mg/m3 of TDI based on a 15-L air sample. This corresponds to 0.15 to 40 ppb(V) and brackets the established TLV value of 5 ppb(v). 1.6 The average correlation coefficient is 0.9999 and 0.9999 for the UV detector, for 2,6 and 2,4-TDI, respectively. For the fluorescence detector, the average correlation coefficient is 0.9803 and 0.9999 for 2,6 and 2,4-TDI, respectively. These values were obtained from seven standard solutions distributed along the calibration curve, each standard being injected six times, with the curve having been done twice by different operators. 1.7 The quantification limit for 2,6-TDI monomers is 0.007 μg/2 mL of desorption solution, which corresponds to 0.0005 mg/m 3 for 15-L sampled air volume for the UV detector. For the fluorescence detector, the quantification limit is 0.003 μg/2 mL of desorption solution, which correspond to 0.0002 mg/m3 for a volume of 15 L collected in air. These values are equal to ten times the standard deviation obtained from ten measurements carried out on a standard solution whose concentration of 0.02 μg/2 mL is close to the expected detection limit. 1.8 The quantification limit for 2,4-TDI monomers is 0.015 μg/2 mL of desorption solution, which corresponds to 0.001 mg/m 3 for 15-L sampled air volume for the UV detector. For the fluorescence detector, the quantification limit is 0.012 μg/2 mL of desorption solution, which corresponds to 0.0008 mg/m3 for a volume of 15 L of collected air. The...