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. Author manuscript; available in PMC: 2020 Jun 1.
Published in final edited form as: J Air Waste Manag Assoc. 2019 Apr 22;69(6):778–788. doi: 10.1080/10962247.2019.1587553

Table 4.

Spearman correlation coefficients (%) between trace gaseous pollutants, particulate matter pollutants, and meteorological variables from Logan, Utah based on 1-hr summaries.a

Pollutant/meteorological
variable
NO2 NO NOx NOy NOzb O3 PM10 PM2.5 PM10-2.5 Wind
speedc
Temperature Humidity Pressure Mixing
heightd
Total
precipitatione
NO2 100 69 95 93 73 −92 75 75 66 −60 −53 34 26 −64 −14
NO 100 85 84 63 −60 69 69 65 −33 −38 7 22 −61 −14
NOx 100 98 74 −87 80 80 72 −54 −51 28 25 −70 −17
NOy 100 83 −84 88 88 79 −54 −55 24 25 −76 −22
NOzb 100 −61 94 95 82 −50 −60 12 21 −77 −31
O3 100 −64 −65 −56 59 47 −44 −21 58 4f
PM10 100 98 94 −44 −53 2f 22 −78 −28
PM2.5 100 87 −47 −57 11 20 −78 −28
PM10-2.5 100 −36 −42 −16 24 −67 −27
Wind speedc 100 49 −50 −6f 42 21
Temperature 100 −20 −57 59 36
Humidity 100 −24 −52 17
Pressure 100 −34 −17
Mixing heightd 100 4f
Total precipitatione 100

Notes. All correlations statistically significant at the 1% level, except as indicated.

a

Sample size varied between 684 and 740, except for variable pairs involving wind speed or mixing height. Excluding mixing height, sample sizes involving wind speed ranged from 508 to 531. Excluding wind speed, sample sizes involving mixing height were between 273 and 286. The value of n for the wind speed/mixing height pair was 193.

b

NOz = NOy – NOx

c

Wind speed had lower data capture (542 of 740 possible hr or 73%).

d

Mixing height suffered from poor data capture (286 of 740 possible hr or 39%).

e

Most of the hours had no precipitation (673 of 740 possible hr or 90%).

f

Not statistically significant (10% level).