Concentration-response to PM2.5

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Question

What is the the quantitative dose-response relationships between outdoor air PM2.5 concentration and mortality due to cardio-pulmonary, lung cancer, and other non-accidental causes (index Cause of death 2)?

Answer

This code gets the ovariable of this page and calculates some basic results.

+ Show code- Hide code library(OpasnetUtils) # A package with Opasnet functionalities library(xtable) # A package with table formats library(ggplot2) # A package with fancy graph formats objects.latest("Op_en2202", "calculations") # Get the latest ovariables from code calculations on page Op_en2202. ConcentrationresponsetoPM2.5 <- EvalOutput(ConcentrationresponsetoPM2.5) print(xtable(ConcentrationresponsetoPM2.5)@output), type = 'html') # Show a result table ggplot(ConcentrationresponsetoPM2.5@output, # Show a bar chart aes(x = Exposuremetric, y = ERFResult)) + geom_bar(position="dodge") + theme_grey(base_size = 24)

Rationale

⇤#: This paper should be included in the text.

• Burnett RT, Pope CA 3rd, Ezzati M, Olives C, Lim SS, Mehta S, Shin HH, Singh G, Hubbell B, Brauer M, Anderson HR, Smith KR, Balmes JR, Bruce NG, Kan H, Laden F, Prüss-Ustün A, Turner MC, Gapstur SM, Diver WR, Cohen A. An integrated risk function for estimating the global burden of disease attributable to ambient fine particulate matter exposure. Environ Health Perspect. 2014 Apr;122(4):397-403. doi:10.1289/ehp.1307049 Epub 2014 Feb 7. Erratum in Environ Health Perspect. 2014 Sep;122(9):A235. [1] [2] --Jouni (talk) 14:19, 26 January 2015 (UTC)

Data

Concentration-response function

Concentration-response to PM2.5(relative increase of mortality per µg/m3)

Obs	Disease	Response metric	Exposure route	Exposure metric	Exposure unit	Threshold	ERF parameter	ERF	Description
1	Cardiopulmonary	Mortality	Inhalation	Annual average outdoor concentration	µq/m3	0	Relative increase	0.0128 (-0.0036-0.0375)	Dockery et al. 1993 and Pope et al. 2002
2	Lung cancer	Mortality	Inhalation	Annual average outdoor concentration	µq/m3	0	Relative increase	0.0150 (-0.0350-0.0728)	Dockery et al. 1993 and Pope et al. 2002
3	Other causes	Mortality	Inhalation	Annual average outdoor concentration	µq/m3	0	Relative increase	0.0008 (-0.0232-0.0252)	Dockery et al. 1993 and Pope et al. 2002
4	All causes	Mortality	Inhalation	Annual average outdoor concentration	µq/m3	0	Relative increase	0.0091 (-0.0019-0.0289)	Dockery et al. 1993 and Pope et al. 2002

PM_2.5 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

In principle the ERFs for long-term exposure (produced by cohort studies) should also capture the mortality effects of short-term exposure (ERFs 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.

Pope et al. (2002)

• 6% increase in the risk of deaths from all causes (excluding violent death) (95% CI 2-11%) per 10 µg/m3 PM2.5 in age group 30+
• 12% increase in the risk of death from cardiovascular diseases and diabetes (95% CI 8-15%) per 10 µg/m3 PM2.5 in age group 30+
• 14% increase in the risk of death from lung cancer (95% CI 4-23%) per 10 µg/m3 PM_2.5 in age group 30+

Woodruff et al (1997)

• 4% (95% Cl 2%-7%) increase in all-cause infant mortality per 10 µg/m3 PM₁₀ (age 1 month to 1 year)

Tuomisto et al. 2008:

• A structured expert judgement study of the population mortality effects of PM_2.5 air pollution.
• Opinions of six European air pollution experts were elicited.
• Percent increase per 1 µg/m³ increase in PM_2.5:
  • Equal-weight decision-maker
    • Best estimate 0.97
    • 95% quantile 4.54
    • 5% quantile 0.02
  • Performance-based decision-maker
    • Best estimate 0.60
    • 95% quantile 3.80
    • 5% quantile 0.06

'Mortality effects of short-term (acute) exposure to ambient air PM

Anderson et al. 2004

• 0.6% (95% Cl 0.4%-0.8%) increase in all-cause mortality (excluding accidents) per 10 µg/m3 PM₁₀ in all ages
• 1.3% (95% Cl 0.5%-2%) increase in respiratory mortality per 10 µg/m3 PM₁₀ in all ages
• 0.9% (95% Cl 0.5%-1.3%) increase in cardiovascular mortality per 10 µg/m3 PM₁₀ in all ages

These coefficients are defined as distributions around estimates of central tendency for each cause of death.

Relative increase of mortality per 1 μgm-3 increase of outdoor PM2.5 concentration. Values were drawn with equal probability from the two distributions reported in ,

Uncertainties:

• Mortality estimate from Hoek et al. (2002) was not included due to many confounding factors related to mortality, e.g. road noise.
• Probability for PM2.5 assumed to be the true cause of the effects in 70 %, 90 %, and 10 % for cardiopulmonary, lung cancer and all other mortality, respectively (author judgement).
• Toxicity differences between ambient air particles and the particles generated by different bus types were not taken into account due to lack of comprehensive data.

• No threshold was assumed in the dose-response relationship.

Calculations

This code defines and stores the ovariable of this page (ConcentrationresponsetoPM2.5).

+ Show code- Hide code library(OpasnetUtils) library(xtable) ConcentrationresponsetoPM2.5<- Ovariable("ConcentrationresponsetoPM2.5 ", ddata = "Op_en2202", getddata = FALSE, save = TRUE) cat("Ovariable ConcentrationresponsetoPM2.5 saved for later use. Page name: Op_en2202, code name: calculations\n") print(xtable(EvalOutput(ConcentrationresponsetoPM2.5)@output), type = "html")

Unit

m³/μg D↷

See also

• Relative risks of mortality -page in Heande
• 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
• NEEDS - New Energy Externalities Developments for Sustainability, Deliverable 3.7 "A set of concentration-response function", Integrated Project, Sixth Framework Programme, Project no. 502687.