Todd
McAlary
*ac,
Hester
Groenevelt
a,
Stephen
Disher
b,
Jason
Arnold
b,
Suresh
Seethapathy
c,
Paolo
Sacco
d,
Derrick
Crump
e,
Brian
Schumacher
f,
Heidi
Hayes
b,
Paul
Johnson
g and
Tadeusz
Górecki
c
aGeosyntec Consultants, Inc., 130 Research Lane, #2, Guelph, Ontario N1G 5G3, Canada. E-mail: tmcalary@geosyntec.com
bEurofins Air Toxics, Inc. (formerly Air Toxics Ltd.), Folsom, CA, USA
cUniversity of Waterloo, Waterloo, Ontario, Canada
dFondazione Salvatore Maugeri, Padova, Italy
eCranfield University, Cranfield, UK
fUnited States Environmental Protection Agency, Las Vegas, NV, USA
gArizona State University, Tempe, AZ, USA
First published on 21st May 2015
Correction for ‘Passive sampling for volatile organic compounds in indoor air-controlled laboratory comparison of four sampler types’ by Todd McAlary et al., Environ. Sci.: Processes Impacts, 2015, 17, 896–905.
Analyte | Revised uptake rate (mL min−1) | ||||
---|---|---|---|---|---|
WMS | Radiello | SKC Ultra | ATD Tube | ATD Tube | |
1.8 mL vial and Anasorb 747 | White body and charcoal | Ultra II and Carbopack X | Carbopack B | Tenax TA | |
a * – Consider field calibration if temperature, humidity, velocity, duration or concentration are considerably different than 21 °C, 60% RH, 0.2 m s−1, 4 days and 50 ppbv, respectively. ** – Field calibration is recommended. | |||||
1,1,1-Trichloroethane | 1.5 | 59* | 11* | 0.36 | 0.34 |
1,2,4-Trimethylbenzene | 7.0* | 57 | 9.0* | 0.45 | 0.43 |
1,2-Dichloroethane | 2.2* | 64 | 9.8* | 0.30* | 0.34* |
2-Butanone (MEK) | 1.5* | 49** | 7.8* | 0.11** | 0.50* |
Benzene | 2.2 | 72 | 15* | 0.60 | 0.37* |
Carbon tetrachloride | 1.8* | 54 | 7.2* | 0.41 | 0.34 |
n-Hexane | 1.5* | 53 | 9.8* | 0.56* | 0.28* |
Naphthalene | 4.4** | 57** | 4.7* | 0.45 | 0.49 |
Tetrachloroethene | 3.9* | 60 | 13 | 0.47 | 0.35 |
Trichloroethene | 2.6* | 63 | 13* | 0.46 | 0.31 |
The Royal Society of Chemistry apologises for these errors and any consequent inconvenience to authors and readers.
This journal is © The Royal Society of Chemistry 2015 |