Particles from Outdoor Air

Particles from Outdoor Air

Ambient particle pollution is an important source of morbidity and mortality [1-5]. Globally, an estimated 3.2 million deaths per year are attributable to ambient particle pollution [6]. A substantial fraction of people’s exposures to particles from outdoor air occurs when people are indoors [7-9]; thus, climate-related changes in outdoor air particle levels will affect indoor particle exposures. There are numerous mechanisms through which climate change is expected to influence outdoor air particles [10]. For example, higher temperatures will speed the chemical reactions that produce some types of particles and also increase emissions of reactive organic chemicals from vegetation that lead to particles. Higher temperatures will also shift the partitioning toward more gases and fewer particles of other types. Increased overall global precipitation with climate change is expected to remove particles from the air, reducing airborne concentrations. Climate change will also affect winds, frequency of drought which influences wind-blown dust, wildfires, and mixing of pollutants in the atmosphere. One recent analysis predicts that climate change will substantially increase the frequency and duration of periods of air stagnation in much of the world, leading to more frequent periods with high concentrations of particles and other air pollutants [11]. At present; however, there is no consensus about the net effects of climate change on overall levels of ambient particles [10, 12-14]. Effects are likely to vary regionally [15]. For North America in 2041 to 2050 relative to 1997-2006, Kelly, Makar [15] predicted quite small increases and decreases in particle concentrations. Given the high level of morbidity and mortality associated with outdoor air particles, even small fractional changes in particle levels could have substantial consequences for health. For the U.S., Tagaris et al. [16] projected 4000 deaths per year from climate-related increases in particles, which far outweighed their estimated 300 deaths per year from climate-related increases in ozone.   

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2.         Pope, C.A., 3rd and D.W. Dockery, Health effects of fine particulate air pollution: lines that connect. J Air Waste Manag Assoc, 2006. 56(6): p. 709-42. https://dx.doi.org/10.1080/10473289.2006.10464485.

3.         Pope, C.A., 3rd, M. Ezzati, and D.W. Dockery, Fine-particulate air pollution and life expectancy in the United States. N Engl J Med, 2009. 360(4): p. 376-86. https://dx.doi.org/10.1056/NEJMsa0805646.

4.         Delfino, R.J., et al., The relationship of respiratory and cardiovascular hospital admissions to the southern California wildfires of 2003. Occupational and Environmental Medicine, 2009. 66(3): p. 189-197. https://dx.doi.org/10.1136/oem.2008.041376.

5.         Delfino, R.J., C. Sioutas, and S. Malik, Potential role of ultrafine particles in associations between airborne particle mass and cardiovascular health. Environ Health Perspect, 2005. 113(8): p. 934-46. https://dx.doi.org/10.1289/ehp.7938.

6.         Lim, S.S., et al., A comparative risk assessment of burden of disease and injury attributable to 67 risk factors and risk factor clusters in 21 regions, 1990-2010: a systematic analysis for the Global Burden of Disease Study 2010. Lancet, 2012. 380(9859): p. 2224-60. https://dx.doi.org/10.1016/s0140-6736(12)61766-8.

7.         Riley, W.J., et al., Indoor particulate matter of outdoor origin: importance of size-dependent removal mechanisms. Environ Sci Technol, 2002. 36(2): p. 200-7. https://dx.doi.org/10.1021/es010723y.

8.         Wallace, L., Indoor particles: a review. Journal of the Air & Waste Management Association, 2012. 46: p. 98-126. https://dx.doi.org/10.1080/10473289.1996.10467451.

9.         Bennett, D. and P. Koutrakis, Determining the infiltration of outdoor particles in the indoor environment using a dynamic model. Journal of Aerosol Science, 2006. 37(6): p. 766-785. https://dx.doi.org/10.1016/j.jaerosci.2005.05.020.

10.       Dawson, J.P., et al., Understanding the meteorological drivers of US particulate matter concentrations in a changing climate. Bulletin of the American Meteorological Society, 2014. 95: p. 521-532. https://dx.doi.org/10.1175/BAMS-D-12-00181.1.

11.       Horton, D.E., et al., Occurrence and persistence of future atmospheric stagnation events. Nature Climate Change, 2014. https://dx.doi.org/10.1038/NCLIMATE2272.

12.       Kirtman, B., et al., Near-term climate change: projections and predictability, in Climate change 2013: the physical science basis. contribution of Working Group I to the fifth assessment report of the Intergovernmental Panel on Climate Change, T.F. Stocker, et al., Editors. 2014, Cambride University Press: Cambridge, United Kingdom.

13.       Melillo, J.M., Richmond T. C. ,  Yohe G. W. , Eds.,, Climate change impacts in the United States: the third national climate assessment. 2014, U.S. Global Change Research Program: Washington, D. C.

14.       USGCRP, The impacts of climate change on human health in the United States: a scientific assessment, A. Crimmins, J. Balbus, J.L. Gamble, C.B. Beard, J.E. Bell, D. Dodgen, R.J. Eisen, N. Fann, M.D. Hawkins, S.C. Herring, L. Jantarasami, D.M. Mills, S. Saha, M.C. Sarofim, J. Trtanj, and L. Ziska Editor. 2016, U.S. Global Change Research Program: Washington, DC Available from: https://www.globalchange.gov/browse/reports/impacts-climate-change-human-health-united-states-scientific-assessment.

15.       Kelly, J., P. Makar, and D. Plummer, Projections of mid-century summer air-quality for North America: effects of changes in climate and precursor emissions. Atmospheric Chemistry & Physics Discussions, 2012. 12(2). https://dx.doi.org/10.5194/acp-12-5367-2012.