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. Author manuscript; available in PMC: 2019 Jan 15.
Published in final edited form as: Ann Allergy Asthma Immunol. 2018 Jan;120(1):96–97.e1. doi: 10.1016/j.anai.2017.10.002

Fig 1. Bivariate analysis of Inspirotec airborne allergen capture compared with two reference methods.

Fig 1.

Reference methods were collection by air sampling and dust sampling. Samples were from twenty-five urban, low income Baltimore homes at baseline, 17 at 3 months, and 12 at 6 months. Whether a home is in the active intervention group or the control group is still blinded. Air sampling by PM10 (particles > 10 μm selectively removed with an impinger) and dust collection were as described elsewhere (5). In parallel, Inspirotec samplers were plugged into wall sockets and run for the same period of 5– 7 days. Inspirotec samplers had pre-calibrated flow rates of 100±20 liters/min and were stable within ±10% over multiple usages. PM10 samplers were adjusted to 4 liters/min. Samples from Inspirotec electrodes and PM10 filters were extracted in 1 mL and assayed by Indoor Biotechnologies MARIA™ assays for the 12 common household allergens: Der p 1, Der f 1, mite group 2, Fel d 1, Can f 1, Mus m 1, Rat n1, Bla g 1, Alt a 1, Bet v 1, Asp f 1, Phl p 5. Dust samples were weighed, extracted by standard methods and assay by Indoor Biotech ELISA for Der f 1, Fel d 1, Can f 1, Mus m 1 and Bla g 2. Air sample results were expressed as pg/m3 and dust as μg/g. JMP® Pro 13.0.0 (SAS Institute Inc.Cary, NC) and StataSE 13.0 (StataCorp LLC, College Station, Texas) statistics packages were used. Allergen variables were log10-transformed and r values shown are Pearson’s rho (r) from StataSE. Because there was repeated sampling within the same home, r and p-values were generated using Generalized Estimating equations, which account for the within-home correlation. The best straight line fit to the log10 of the values are shown. Values below the LLOD were assigned a value of LLOD/2.