Low molecular weight carbonyls in large midwestern office buildings

Airborne carbonyls in large office buildings in the Midwestern United State s have been studied both indoors and near the air-intakes environment using HPLC and GCMS methods. Air sampling for carbonyls was conducted using 2,4- dinitrophenylhydrazine coated silica gel cartridges and stainless steel Ten ax TA(R) tubes. 1,3-dinitrobenzene, 2,4-dinitrophenol and 2,4-dinitroanilin e were tentatively identified as degradation products of 2,4-dinitrophenylh ydrazine by HPLC and GCMS analysis. Performance of the Tenax TA(R)-GCMS met hod under field sampling. conditions was studied and Tenax TA(R) data was v alidated, to estimate the lowest possible concentration of carbonyls in the environment, using a correction term derived from error propagation analys is. Analytical recovery, analytes' breakthrough percentage, and limitations of the DNPH-cartridge sampling are presented along with GCMS ion fragmenta tion data of the tentatively identified product(s). Carbonyls including for maldehyde (6.8 +/- 8.8 ppbv),(+) acetaldehyde (2.8 +/- 3.2 ppbv), acetone ( 4.7 +/- 8.9 ppbv), methyl ethyl ketone (0.4 +/- 0.7 ppbv), 4-methyl-2-penta none (0.5 +/- 1.7 ppbv), n-hexanal(0.2 +/- 0.6 ppbv) and n-heptanal (0.2 +/ - 1.8 ppbv) were present in indoor air. Outdoor concentrations were: formal dehyde, 2.1 +/- 3.1 ppbv; acetaldehyde, 2.2 +/- 2.4 ppbv; acetone, 1.4 +/- 3.1 ppbv; methyl ethyl ketone, 0.6 +/- 0.4 ppbv; 4-methyl-2-pentanone, 0.2 +/- 0.1 ppbv: n-hexanal, 0.2 +/- 0.5 ppbv; and n-heptanal (0.2 +/- 0.4 ppbv ). Total carbonyl concentrations (Sigma(CO)) were 15.6 +/- 13.2 ppbv and 6. 9 +/- 5.1 ppbv in indoor and outdoor air respectively. Average formaldehyde levels (7ppbv) in non-complaint buildings were lower than the recommended concentration levels in indoors of residential environment (100 ppbv). ppbv = (ng . L-1) . 24.45/(molecular weight).