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. 2017 May 9;12(5):e0177263. doi: 10.1371/journal.pone.0177263

Table 1. Description of environmental fungal loads collected by HTSTs and viable impaction sampler.

  Outdoor air collected by HTST-O1
n = 28 days
Outdoor air collected by HTST-O2
n = 28 days
Outdoor air collected by HTST-C
n = 30 days
Indoor air collected by HTST-I
n = 28 days
Indoor air collected by viable impaction sampler
n = 19 days
Wilcoxon statistic (P-value)c
  HTST-O1 versus HTST-O2 HTST-O2 versus HTST-I HTST-I versus viable impaction sampler
Median TFLa, (IQR)b 3,025.0
(2,056.3–4,381.3)
3,287.5
(1,768.8–5,768.8)
3,625.0
(2,425.0–5,500.0)
850.0
(687.5–1,162.5)
100.0
(37.5–155.0)
169.5 (0.6) 6.5 (<0.01) 171 (<0.01)
Median AFL or Aspergillus spp. loada, (IQR)b 100.0
(0.0–125.0)
100.0
(0.0–162.5)
125.0
(0.0–200.0)
0.0
(0.0–0.0)
5.0
(0.0–10.0)
28.5 (0.9) 1 (0.05) 12 (0.01)

NOTE: AFL: Aspergillaceae fungal load, HTST: Hirst-type spore trap, IQR: Interquartile range. TFL: Total fungal load.

aIndoor air collected by HTSTs was expressed in AFLs, and indoor air collected by viable impaction sampler was expressed in Aspergillus spp. load.

bExpressed in particles/m3 for HTSTs with conversion factor 25.7 and in CFU/m3 for viable impaction sampler.

cWilcoxon statistics and P-values calculated with Wilcoxon’s paired signed-rank test.