Table 1. Emission rates of known THS compounds in online PTR-TOF MS data.
Compounds |
Average emission rate during THS events (mg/hour) |
Emission rate regression to 2,5-dimethylfuran |
Emission rate regression to benzene |
t test: R-rated versus G-rated emission rates |
||||
Mean ± SD* | r | Slope | r | Slope | t | P value† | ||
Aromatics | Benzene‡§ | 3.46 ± 1.79 | 0.87 | 4.73 ± 0.73 | 1.00 | 1.00 ± 0.00 | 4.14 | 0.001 |
Toluene‡§ | 5.91 ± 2.78 | 0.74 | 6.14 ± 1.53 | 0.93 | 1.42 ± 0.15 | 2.79 | 0.009 | |
C8 aromatics‡§ | 4.84 ± 2.11 | 0.74 | 5.00 ± 1.26 | 0.92 | 1.15 ± 0.14 | 2.81 | 0.010 | |
C9 aromatics‡ | 3.12 ± 1.37 | 0.72 | 3.28 ± 0.88 | 0.91 | 0.77 ± 0.10 | 4.36 | <0.001 | |
C10 aromatics‡ | 0.91 ± 0.42 | 0.75 | 1.03 ± 0.25 | 0.91 | 0.23 ± 0.03 | 4.62 | <0.001 | |
Phenol‡§ | 0.57 ± 0.32 | 0.85 | 0.74 ± 0.13 | 0.77 | 0.13 ± 0.03 | 2.60 | 0.011 | |
Styrene‡§ | 0.71 ± 0.35 | 0.72 | 0.84 ± 0.22 | 0.83 | 0.18 ± 0.03 | 5.07 | <0.001 | |
Benzaldehyde‡ | 0.24 ± 0.10 | 0.59 | 0.18 ± 0.07 | 0.57 | 0.03 ± 0.01 | 2.98 | 0.006 | |
Cresols‡§ | 0.26 ± 0.14 | 0.87 | 0.34 ± 0.05 | 0.81 | 0.06 ± 0.01 | 2.93 | 0.006 | |
Naphthalene‡§ | 0.34 ± 0.16 | 0.88 | 0.40 ± 0.06 | 0.88 | 0.07 ± 0.01 | 2.78 | 0.008 | |
Furanoids | Furan | 0.43 ± 0.40 | 0.90 | 0.90 ± 0.12 | 0.74 | 0.14 ± 0.03 | 1.83 | 0.045 |
2-Methylfuran | 0.83 ± 0.75 | 0.98 | 1.92 ± 0.11 | 0.85 | 0.31 ± 0.05 | 3.15 | 0.006 | |
2,5-Dimethylfuran§ | 0.48 ± 0.36 | 1.00 | 1.00 ± 0.00 | 0.87 | 0.16 ± 0.02 | 3.76 | 0.002 | |
Furfural‡ | 0.60 ± 0.36 | 0.90 | 0.86 ± 0.11 | 0.80 | 0.14 ± 0.03 | 2.29 | 0.020 | |
Furfuryl alcohol‡ | 0.31 ± 0.14 | 0.93 | 0.37 ± 0.04 | 0.83 | 0.06 ± 0.01 | 3.37 | 0.003 | |
Carbonyls | Formaldehyde§ | 0.94 ± 0.50 | 0.87 | 1.25 ± 0.20 | 0.83 | 0.22 ± 0.04 | 3.84 | 0.001 |
Acetaldehyde§ | 9.07 ± 6.51 | 0.90 | 15.44 ± 2.20 | 0.84 | 2.64 ± 0.50 | 2.86 | 0.009 | |
Acrolein§ | 0.73 ± 0.57 | 0.94 | 1.43 ± 0.14 | 0.87 | 0.24 ± 0.04 | 3.31 | 0.004 | |
Acetone∥ | 20.45 ± 10.45 | 0.69 | 19.54 ± 6.43 | 0.72 | 3.75 ± 1.14 | 3.06 | 0.010 | |
Methacrolein | 0.61 ± 0.43 | 0.93 | 1.10 ± 0.12 | 0.85 | 0.18 ± 0.03 | 3.14 | 0.004 | |
2,3-Butanedione | 1.00 ± 0.68 | 0.90 | 1.68 ± 0.23 | 0.72 | 0.25 ± 0.07 | 3.59 | 0.003 | |
Other | Acetonitrile§ | 1.20 ± 0.86 | 0.96 | 2.24 ± 0.19 | 0.80 | 0.35 ± 0.07 | 3.27 | 0.004 |
Acetic acid∥ | 8.40 ± 2.21 | 0.68 | 5.84 ± 1.99 | 0.69 | 1.09 ± 0.36 | 3.10 | 0.010 | |
Isoprene | 4.55 ± 2.89 | 0.84 | 6.81 ± 1.22 | 0.77 | 1.15 ± 0.26 | 2.93 | 0.006 | |
Monoterpenes‡∥ | 2.14 ± 1.91 | 0.58 | 2.62 ± 1.05 | 0.46 | 0.41 ± 0.23 | 0.99 | 0.179 |
*Emission rates were calculated from the THS emission events of 10 R-rated movie showings unless noted otherwise. High SDs indicate high movie-to-movie variability. Emission rates include isomers and ionization products not mentioned above (e.g., methyl vinyl ketone with methacrolein).
†P values in bold represent those that are statistically significant (P < 0.05) for the unpaired two-sample t test, evaluating whether the emission rates were higher in the 10 R-rated movie screenings than the five family movies. See section S1 for more details.
‡Compounds were identified with an offline GC-MS method for ≥C6 compounds using standards and the National Institute of Standards and Technology library.
§Hazardous air pollutants (HAPs) as assigned by the EPA or in the case of 2,5-dimethylfuran, showed cytotoxicity in previous studies (1).
∥Emission factors use data from days 1 to 3 for acetone and acetic acid because large non-THS related emissions from cleaning were observed before the start of day 4 for these compounds, which biased calculations. The monoterpenes values exclude the third film on day 1 because of a large non-THS spike after the start of the film.