Skip to main content
. Author manuscript; available in PMC: 2016 Nov 21.
Published in final edited form as: Res Rep Health Eff Inst. 2012 Dec;(172):5–82.

Table 11.

Comparison of Yard Upwind Values with Other Studies of Neighborhoods

Yard
Upwind
RIOPA Study
Outdoor
Samplesa
Minneapolis
Neighborhoodsb
New York
Inner City
Neighborhoodc,d
Los Angeles
Inner City
Neighborhoodc
Brisbane
Eagle Farm
Light Industrye



Winter / Summer Winter / Summer Winter / Summer






Pollutant
(µg/m3)
N Median SD N Median SD N Median SD N Median 90th
Per-
centile
N Median SD N Median SD
1,3-Butadiene 432 0.12 0.45 31
27
0.1
0.1
0.2
0.4
35
32
0.2
0.01
0.4
Benzene 432 1.01 0.87 554 2.15 2.11 113 1.3
1.1
2.2
1.6
31
27
2.4
1.1
1.2
1.1
35
32
4.3
2.3
1.7
0.8
28 10.5 31.9
Ethylbenzene 432 0.40 0.53 554 1.29 1.87 113 0.6
0.5
0.8
0.7
31
26
1.1
1.7
0.5
1.6
35
32
2.9
2.1
1.4
0.7
28 5.9 40.3
Toluene 432 2.77 3.43 554 7.09 6.47 113 2.6
2.7
4.2
3.6
31
26
5.5
6.9
2.7
3.5
35
32
16
11
9.4
3.8
28 40.0 312.9
m&p-Xylenes 432 1.36 1.69 554 3.57 4.15 113 2.3
2.0
3.3
2.8
31
27
3.7
5.0
1.7
5.4
35
32
11
7.8
5.1
2.5
28 21.2 121.5
o-Xylene 432 0.46 0.63 554 1.48 3.90 113 0.8
0.7
1.1
0.9
31
27
1.3
1.8
0.6
1.7
35
32
3.9
2.8
1.9
0.9
28 8.3 52.1
Acetaldehydef 345 2.06 2.45 395 3.21 1.65 36
36
2.8
4.2
0.9
1.5
40
35
3.7
4.1
1.2
1.6
28 2.9 4.0
Formaldehydef 345 3.22 1.75 395 3.02 3.00 36
36
2.1
5.3
0.9
2.3
40
35
3.9
4.4
1.3
1.6
28 1.8 2.8
f

Aldehydes were collected by passive sampling using the DNSH method (Herrington et al. 2005).