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Summary
2006, Vol. 18, No. 8, Pages 541-547
Vehicular Air Pollution, Playgrounds, and Youth Athletic FieldsKenneth W. Rundell, PhD, Renee CavistonHuman Performance Laboratory, Keith J. O'Neill Center for Healthy Families, Marywood University, Scranton, Pennsylvania, USA In spite of epidemiological evidence concerning vehicular air pollution and adverse respiratory/cardiovascular health, many athletic fields and school playgrounds are adjacent to high traffic roadways and could present long-term health risks for exercising children and young adults. Particulate matter (PM1,0.02–1.0 μm diameter) number counts were taken serially at four elementary school athletic/playground fields and at one university soccer field. Elementary school PM1 measurements were taken over 17 days; measurements at the university soccer field were taken over 62 days. The high-traffic-location elementary school field demonstrated higher 17-day [PM1] than the moderate and 2 low traffic elementary school fields (48,890 ± 34,260, 16,730 ± 10,550, 11,960 ± 6680, 10,030 ± 6280, respective mean counts; p < .05). The 62-day mean PM1 values at the university soccer field ranged from 115,000 to 134,000 particles cm− 3. Lowest mean values were recorded at measurement sites furthest from the highway ( Forward Links to Citing ArticlesKenneth W. Rundell, Josh B. Slee, Renee Caviston, Amanda M. Hollenbach. (2008) Decreased Lung Function After Inhalation of Ultrafine and Fine Particulate Matter During Exercise is Related to Decreased Total Nitrate in Exhaled Breath Condensate. Inhalation Toxicology 20:1, 1-9 Online publication date: 1-Jan-2008. Summary | Full Text | PDF (551 KB) | PDF Plus (538 KB) Bijaya Padhi, Pratap Padhy. (2008) Assessment of Intra-urban Variability in Outdoor Air Quality and its Health Risks. Inhalation Toxicology 20:11, 973-979 Online publication date: 1-Jan-2008. Summary | Full Text | PDF (1644 KB) | PDF Plus (1698 KB) |
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34,000 particles cm− 3) and followed a second-order logarithmic decay (R2 = .999) with distance away from the highway. Mean NO2 and SO2 levels were below 100 ppb, mean CO was 0.33 ± 1.87 ppm, and mean O3 was 106 ± 47 ppb. Ozone increased with rising temperature and was highest in the warmer afternoon hours (R = .61). Although the consequence of daily recess play and athletic activities by school children and young athletes in high ambient [PM1] conditions has not yet been clearly defined, this study is a critical component to evaluating functional effects of chronic combustion-derived PM exposure on these exercising schoolchildren and young adults. Future studies should examine threshold limits and mechanistic actions of real-world particle exposure.
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