Author Correction: Cabin air quality on non‐smoking commercial flights: A review of published data on airborne pollutants

Correction to: Indoor Air https://onlinelibrary.wiley.com/doi/10.1111/ina.12831, published on April 2021. In the version of this article initially published, there are some errors which are listed below including the correction list: We reviewed 47 documents published 1967–2019 that reported measurements of volatile organic compounds (VOCs) on commercial aircraft. We compared the measurements with the air quality standards and guidelines for aircraft cabins and in some cases buildings. change to We reviewed 47 documents published 1967–2019 that reported measurements of volatile organic compounds (VOCs) on commercial aircraft. We compared the measurements with the air quality standards and guidelines for aircraft cabins and in some cases buildings to assess the importance of exposures. “PM was measured in 17 studies on a total of 451 flights” should read “PM was measured in 17 studies on a total of 511 flights” Crump et al.70 2011 included 40 flights with particulate measurements should read Crump et al.70 2011 included 100 flights with particulate measurements Number of flights - 451 should read Number of flights - 511 Avg. should read Mean The presence of a range of SVOCs in aircraft cabin and cockpit air has been recorded in several studies69,80,85,89,112-117. The cabin air supply in most jet aircraft is obtained by extraction of heated and compressed bleed air from the jet engine cores, prior to mixing with filtered recycled cabin air. Furthermore, the aircraft hydraulic reservoir vent is connected to the cabin air ventilation system, making it possible for hydraulic oil aerosols to enter cabin air118; they also have other sources as shown by Schuchardt et al.89. change to The presence of a range of SVOCs in aircraft cabin and cockpit air has been recorded in several studies69,80,85,89,112-117. The cabin air supply in most jet aircraft is obtained by extraction of heated and compressed bleed air from the jet engine cores, prior to mixing with filtered recycled cabin air. There are events when aircraft engine lubricant containing tricresyl phosphates (TCPs) contaminate aircraft cabins118. There are also other sources of SVOCs as shown by Schuchardt et al.89. Avg. should read Mean Medium should read Median Note: concentration (average, SD, average minimum, average medium, average maximum) should read Note: concentration (mean, SD, average minimum, average medium, average maximum). US92 should read US93. Japan105 should read Japan106. China106 should read China107. Canada107 should read Canada108. WHO93 should read WHO94. Threshold limit value109 should read Threshold limit value110. NIOSH/OSHA110 should read NIOSH/OSHA111. 1410 should read 2350 Avg. should read Mean (with no events and with events). The SVOCs with high concentrations and high frequency of detection were naphthalene (average concentration 1,241±166 ng/m3), tributyl phosphate (TiBP) (average concentration 495±59 ng/m3), tris (chloro-isopropyl) phosphate (TCPP) (average concentration 506±0.4 ng/m3), and trichloroethylene (TCE) (average concentration 483±36 ng/m3); it is worth mentioning that tributyl phosphate (TiBP) was also detected on discarded cabin air filters at 1 mg/g carbon for filters that had been used for 660 flight hours and at 2 mg/g carbon for filters that had been used for 3937 flight hours101. should read The SVOCs with high concentrations and high frequency of detection were naphthalene (mean ± SD, 1,241±166 ng/m3), tributyl phosphate (TBP) (mean ± SD, 495±59 ng/m3), and tris (chloro-isopropyl) phosphate (TCPP) (mean ± SD, 506±0.4 ng/m3); it is worth mentioning that TBP was also detected on discarded cabin air filters at 1 mg/g carbon for filters that had been used for 660 flight hours and at 2 mg/g carbon for filters that had been used for 3937 flight hours101. 0.1 mg/m3 [skin]111 0.1 mg/m3 8 h110 11 mg/m3 120 2.38 mg/m3 8h110 9 μg/m3 C93 10 μg/m3 1 year94,108 2 mg/m3 120 57.8 mg/m3 8 h110 85.7 mg/m3 15 min110 0.05 mg/m3 109 0.005 mg/m3 109 0.1 mg/m3 NIOSH10 h111 0.2 mg/m3 OSHA 8 h111 0.1 mg/m3 NIOSH 10 h 111 0.2 mg/m3 OSHA 8 h 111 0.1 mg/m3 NIOSH 10 h111 0.2 mg/m3 OSHA 8 h111 Add the following note: When calculating averages, the values below detection limits were considered as 0 The maximum measured levels of CO concentration were higher than the permissible level for 15-minute exposures. should read The occasional 5-minute average levels of CO concentration ranging as high as 9.4 ppm (Table S13) were close to the recommended level for 10-minute TWA exposure (9 ppm) in ASHRAE Standard 16136. 110. NIOSH. NIOSH pocket guide to chemical hazards; 2005. should read NIOSH. NIOSH pocket guide to chemical hazards. https://www.cdc.gov/niosh/npg/ Accessed 2020. 119. RGS. should read 119. TRGS. 128. Sawa Y, Matsueda H, Makino Y, et al. Aircraft observation of CO2, CO2 O3 and H2 over the North Pacific during the PACE-7 Campaign. Tellus B Chem Phys Meteorol. 2004;56(1):2–20. https://doi.org/10.3402/tellu sb.v56i1.16402 should read Sawa Y, Matsueda H, Makino Y, et al. Aircraft observation of CO2, CO, O3 and H2 over the North Pacific during the PACE-7 Campaign. Tellus B Chem Phys Meteorol. 2004;56(1):2–20. https://doi.org/10.3402/tellu sb.v56i1.16402 Insert the reference 90 (see below) after reference 89 (Schuchardt et al. 2019) on page 30. And then reference numbering should be 90 should read 91, 91 should read 92 …… until 137 should read 138. 90. Guan J, Jia Y, Wei Z, Tian X. Temporal variations of ultrafine particle concentrations in aircraft cabin: A field study. Building and Environment. 2019;153(none):118–127. http://dx.doi.org/10.1016/j.buildenv.2019.02.025. A new file with Supplementary Information was placed online. The major changes were made in Table S13 (headings and data regarding CO). In other tables, mean and median were used instead of average and medium. References 90, 111, and 129 were updated. The peer review history for this article is available at https://publons.com/publon/10.1111/ina.12977. The peer review history for this article is available at https://publons.com/publon/10.1111/ina.12977. Please note: The publisher is not responsible for the content or functionality of any supporting information supplied by the authors. Any queries (other than missing content) should be directed to the corresponding author for the article.