Difference between revisions of "ERF of PM2.5 on mortality in general population"
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===Data=== | ===Data=== | ||
| − | '''PM<sub>2.5</sub>''' are fine particles less than 2.5 μm in diameter. Exposure-response function can be derived from exposure modelling, animal toxicology, small clinical or panel studies, and epidemiological studies. Exposed population can be divided into subpopulations (e.g. adults, children, infants, the elderly), and exposure is assessed per certain | + | '''PM<sub>2.5</sub>''' are fine particles less than 2.5 μm in diameter. Exposure-response function can be derived from exposure modelling, animal toxicology, small clinical or panel studies, and epidemiological studies. Exposed population can be divided into subpopulations (e.g. adults, children, infants, the elderly), and exposure is assessed per certain time period (e.g. daily or annual exposure). |
*Health effects related to '''short-term exposure''' | *Health effects related to '''short-term exposure''' | ||
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*14% increase in the risk of death from lung cancer (95% CI 4-23%) | *14% increase in the risk of death from lung cancer (95% CI 4-23%) | ||
per each 10 µg/m<sup>3</sup> elevation in PM<sub>2.5</sub> air pollution | per each 10 µg/m<sup>3</sup> elevation in PM<sub>2.5</sub> air pollution | ||
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| + | In principle the ERFs for long-term exposure (produced by cohort studies) should also capture the mortality effects of short-term exposure (produced by time-series studies). In practice it is likely that they do not do so fully. This is due to the so-called "harvesting" phenomenon, i.e. it is possible that acute exposure, at least to some extent, only brings forward deaths that would have happened shortly in any case. However, adding effects of acute exposure to effects of long-term exposure is problematic because the risk of double-counting. <ref>[http://ec.europa.eu/environment/archives/air/cafe/pdf/cba_methodology_vol2.pdf Service Contract for Carrying out Cost-Benefit Analysis of Air Quality Related Issues, in particular in the Clean Air for Europe (CAFE) Programme. Volume 2: Health Impact Assessment. AEA Technology Environment, 2005.]</ref> | ||
=== Unit === | === Unit === | ||
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*[http://www.euro.who.int/document/E83080.pdf Health aspects of air pollution. Results from the WHO project "Systematic review of health aspects of air pollution in Europe". World Health Organization, 2004.] | *[http://www.euro.who.int/document/E83080.pdf Health aspects of air pollution. Results from the WHO project "Systematic review of health aspects of air pollution in Europe". World Health Organization, 2004.] | ||
*Pope et al. 2004. Cardiovascular mortality and long-term exposure to particulate air pollution. Circulation (109), 71-77. | *Pope et al. 2004. Cardiovascular mortality and long-term exposure to particulate air pollution. Circulation (109), 71-77. | ||
| − | |||
*[http://aje.oxfordjournals.org/cgi/content/full/kwn232v1Robin C. Puett, Joel Schwartz, Jaime E. Hart, Jeff D. Yanosky, Frank E. Speizer, Helen Suh, Christopher J. Paciorek, Lucas M. Neas and Francine Laden: Chronic Particulate Exposure, Mortality, and Coronary Heart Disease in the Nurses’ Health Study. American Journal of Epidemiology, doi:10.1093/aje/kwn232] | *[http://aje.oxfordjournals.org/cgi/content/full/kwn232v1Robin C. Puett, Joel Schwartz, Jaime E. Hart, Jeff D. Yanosky, Frank E. Speizer, Helen Suh, Christopher J. Paciorek, Lucas M. Neas and Francine Laden: Chronic Particulate Exposure, Mortality, and Coronary Heart Disease in the Nurses’ Health Study. American Journal of Epidemiology, doi:10.1093/aje/kwn232] | ||
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Scope
ERF of PM2.5 on mortality in general population describes the relationship between PM2.5 exposure and specific causes of mortality in general adult population. The variable focuses but is not limited to long-term exposure.
Definition
Data
PM2.5 are fine particles less than 2.5 μm in diameter. Exposure-response function can be derived from exposure modelling, animal toxicology, small clinical or panel studies, and epidemiological studies. Exposed population can be divided into subpopulations (e.g. adults, children, infants, the elderly), and exposure is assessed per certain time period (e.g. daily or annual exposure).
- Health effects related to short-term exposure
- respiratory symptoms
- adverse cardiovascular effects
- increased medication usage
- increased number of hospital admissions
- increased mortality
- Health effects related to long-term exposure (more relevance to public health)
- increased incidence of respiratory symptoms
- reduction in lung function
- increased incidence of chronic obstructive pulmonary disease (COPD)
- reduction in life expectancy
- increased cardiopulmonary mortality
- increased lung cancer mortality
Sensitive subgroups: children, the elderly, individuals with heart and lung disease, individuals who are active outdoors.
Mortality effects of long-term (chronic) exposure to ambient air PM
Pope et al. (2002) [1]
- 6% increase in the risk of deaths from all causes (95% CI 2-11%)
- 12% increase in the risk of death from cardiovascular diseases and diabetes (95% CI 8-15%)
- 14% increase in the risk of death from lung cancer (95% CI 4-23%)
per each 10 µg/m3 elevation in PM2.5 air pollution
In principle the ERFs for long-term exposure (produced by cohort studies) should also capture the mortality effects of short-term exposure (produced by time-series studies). In practice it is likely that they do not do so fully. This is due to the so-called "harvesting" phenomenon, i.e. it is possible that acute exposure, at least to some extent, only brings forward deaths that would have happened shortly in any case. However, adding effects of acute exposure to effects of long-term exposure is problematic because the risk of double-counting. [2]
Unit
Relative risk (RR) per 10 µg/m3 change in PM2.5
Result
ERF for chronic PM2.5 exposure
| Cause of death | RR | 95% Cl |
|---|---|---|
| All-cause | 1.06 | 1.02-1.11 |
| Cardiopulmonary | 1.09 | 1.03-1.16 |
| Lung cancer | 1.14 | 1.04-1.23 |
See also
- Health aspects of air pollution. Results from the WHO project "Systematic review of health aspects of air pollution in Europe". World Health Organization, 2004.
- Pope et al. 2004. Cardiovascular mortality and long-term exposure to particulate air pollution. Circulation (109), 71-77.
- C. Puett, Joel Schwartz, Jaime E. Hart, Jeff D. Yanosky, Frank E. Speizer, Helen Suh, Christopher J. Paciorek, Lucas M. Neas and Francine Laden: Chronic Particulate Exposure, Mortality, and Coronary Heart Disease in the Nurses’ Health Study. American Journal of Epidemiology, doi:10.1093/aje/kwn232
References
- ↑ *Pope CA III, Burnett RT, Thun MJ, Calle EE, Krewski D, Ito K & Thurston KD (2002). Lung cancer, cardiopulmonary mortality, and long-term exposure to fine particulate air pollution. JAMA 287(9), 1132-1141.
- ↑ Service Contract for Carrying out Cost-Benefit Analysis of Air Quality Related Issues, in particular in the Clean Air for Europe (CAFE) Programme. Volume 2: Health Impact Assessment. AEA Technology Environment, 2005.
