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Table 3 Distribution of the daily number of ER admissions for respiratory diseases and daily concentrations of chemical air pollution and aeroallergens during the study period, according to the potential confounders considered in the analysisa

From: Air pollution, aeroallergens and admissions to pediatric emergency room for respiratory reasons in Turin, northwestern Italy

 

ER admissions (counts)

PM2.5 (μg/m3)

NO2 (μg/m3)

O3 (μg/m3)

Aeroallergens (grains/m3)

Day of the week

     

 Monday

22.7 ± 10.2

30.4 ± 26.5

47.2 ± 25.1

38.2 ± 27.7

12.7 ± 20.9

 Tuesday

21.4 ± 9.8

30.8 ± 25.4

50.3 ± 24.5

37.8 ± 28.6

14.9 ± 28.8

 Wednesday

20.4 ± 9.6

32.5 ± 25.4

51.0 ± 23.8

38.9 ± 29.2

18.8 ± 38.1

 Thursday

21.6 ± 9.7

35.1 ± 27.8

52.9 ± 25.9

38.9 ± 30.2

15.1 ± 23.0

 Friday

23.4 ± 11.1

33.3 ± 25.0

50.9 ± 24.7

39.9 ± 29.7

17.2 ± 32.1

 Saturday

31.1 ± 12.4

31.5 ± 26.0

45.0 ± 25.1

42.2 ± 29.8

18.2 ± 33.4

 Sunday

32.2 ± 12.8

30.4 ± 27.4

40.9 ± 24.0

41.3 ± 28.5

15.8 ± 27.4

  p

<0.001

0.79

0.002

0.87

0.73

Holidays

     

 Christmas and Easter

47.6 ± 17.5

25.4 ± 15.2

45.1 ± 27.5

32.0 ± 29.9

1.0 ± 1.9

 3 days before/after Christmas and Easter

34.9 ± 16.3

37.9 ± 21.7

58.6 ± 25.8

25.7 ± 23.7

6.4 ± 15.8

 Other holidays

35.6 ± 15.6

37.4 ± 27.7

49.3 ± 22.7

32.2 ± 30.4

12.6 ± 1.9

 Other days

23.8 ± 10.9

31.6 ± 26.4

48.0 ± 25.0

40.4 ± 29.1

16.6 ± 30.2

 p

<0.001

0.39

0.23

0.02

0.20

Influenza outbreaks

     

 No

19.9 ± 9.0

22.8 ± 21.0

36.8 ± 16.9

55.2 ± 27.4

23.8 ± 31.9

 Yes

31.0 ± 12.0

43.9 ± 27.5

63.0 ± 25.8

19.9 ± 16.4

6.3 ± 23.0

 p

<0.001

<0.001

<0.001

<0.001

<0.001

Summer population decrease

    

 2 weeks around 15 August

13.4 ± 4.71

15.8 ± 5.6

20.7 ± 6.3

66.1 ± 15.4

34.7 ± 28.5

 From 16/7 to 31/8 (except 2 weeks around 15 August)

14.4 ± 5.8

14.5 ± 6.4

26.1 ± 8.5

78.0 ± 19.3

29.1 ± 31.6

 Other days

26.4 ± 11.6

34.5 ± 27.1

52.5 ± 24.5

33.7 ± 26.3

13.4 ± 28.7

 p

<0.001

<0.001

<0.001

<0.001

<0.001

Temperatureb (°C)

     

 −6.4, 6.4

29.1 ± 11.6

57.3 ± 28.3

78.9 ± 27.6

12.1 ± 8.8

0.8 ± 2.5

 6.5, 12.8

28.1 ± 11.3

31.7 ± 21.5

51.7 ± 15.2

23.3 ± 17.3

10.1 ± 31.9

 12.9, 20.3

24.8 ± 11.5

27.5 ± 23.9

43.4 ± 17.1

41.2 ± 20.2

14.9 ± 21.6

 20.4, 28.5

19.5 ± 8.2

14.9 ± 6.8

29.4 ± 9.5

73.7 ± 18.4

32.5 ± 39.7

 p

<0.001

<0.001

<0.001

<0.001

<0.001

Cumulative precipitation

    

 <1 mm

25.4 ± 11.4

35.5 ± 28.0

51.5 ± 26.2

38.0 ± 33.7

16.0 ± 29.9

 ≥1 mm

25.2 ± 11.5

25.5 ± 19.2

45.0 ± 20.1

33.7 ± 26.0

9.5 ± 27.3

 p

0.87

<0.001

0.01

0.10

0.02

Relative humidity b(%)

    

 30.4, 60.4

26.4 ± 10.3

17.8 ± 13.1

41.6 ± 17.9

52.1 ± 24.6

25.1 ± 34.3

 60.5, 68.6

23.1 ± 11.6

25.5 ± 18.9

43.2 ± 22.2

50.9 ± 31.3

21.8 ± 37.5

 68.7, 76.4

25.3 ± 11.3

44.7 ± 30.5

56.9 ± 32.1

28.3 ± 23.0

9.6 ± 25.4

 76.5, 85.5

26.7 ± 12.1

42.5 ± 28.8

58.4 ± 22.1

16.7 ± 15.9

1.9 ± 6.0

 p

0.01

<0.001

<0.001

<0.001

<0.001

  1. amean ± SD reported; overall p-values were calculated using non-parametric Kruskall-Wallis tests, under the null hypothesis that the distribution of a variables is homogeneous among the strata of a potential confounder
  2. b coded in groups according to the quartiles of their frequency distribution