Air quality modeling and mortality impact of fine particles reduction policies in Spain
Introduction
The epidemiological literature has signaled that exposure to air pollution, especially fine particles of less than 2.5 µm in aerodynamic diameter (hereinafter referred to as “fine particles”), can lead to cases of immediate (acute) or delayed (chronic) premature death, from cardiopulmonary diseases in particular (Pope and Dockery, 2006; Valavanidis et al., 2008). Epidemiological cohort studies, both in Europe (Beelen et al., 2008, Cesaroni et al., 2013) and in North America (Pope et al., 2002, Turner et al., 2011), have estimated the long-term health risk posed by exposure to air pollution. The Harvard Six Cities study reported a 14% increase in long-term all-cause mortality for every increase of 10 µg/m3 in fine particle concentration (Lepeule et al., 2012). This last study and other recent European cohort studies (Cesaroni et al., 2013, Raaschou-Nielsen et al., 2013a) have reported increases in long-term mortality even at fine particle levels below the ambient air quality standards.
Evidence from a growing body of epidemiological studies has historically supported critical environmental policy decisions (Fann et al., 2011). Assessments of interventions which improve air quality show that a decrease in fine particle levels is accompanied by substantial health benefits (van Erp et al., 2008). By way of example, the 1990 ban on the use of coal in Dublin (Ireland) led to a 70% reduction in monthly mean particle concentrations, and a 6%, 15% and 10% decrease in all-cause, respiratory and heart disease mortality rates, respectively (Clancy et al., 2002).
Health impact assessment makes it possible to quantify the effect that public policies may have on the health of the population (WHO, 2000). Quantitative risk assessment methods are useful in providing point estimates, or a range of estimates, for the health risks associated with a variety of hazards, including air pollution, and are often used in health-based policy making (O’Connell and Hurley, 2009). For health impact assessment purposes, air quality information must be linked to the population subject to the exposure. The application of air quality models helps to examine potential air quality impacts and related health effects associated with emissions, and develop country-wide health impact assessment, especially in study areas without air pollution monitoring data (Dhondt et al., 2012).
In Spain, the Air Pollution Risk Assessment System (Sistema de Evaluación de Riesgos por Contaminación Atmosférica – SERCA) research project pioneered a nation-wide health impact assessment of air pollution, based on a reduction in fine particle levels in 2011 vis-à-vis 2004, as a result of a series of air quality control measures. Although such policy measures are not necessarily focused on health, they could nonetheless have an indirect effect on health. This study estimated that 1718 annual deaths were attributable to an average annual reduction of 0.7 µg/m3 in fine particle levels in Spain (Boldo et al., 2011). The experience and knowledge acquired in this first stage of the project was used to undertake a new nation-wide health impact assessment, with more accurate estimates and a time horizon extended to 2014. This study now shows the impact of various air quality control measures on mortality, taking fine particle concentrations as an overall indicator of air pollution (WHO, 2006). In addition to total mortality, the study analyzes the impact of changes in fine particle levels on two of the leading principal causes of death in Spain (INE, 2013), namely, ischemic heart disease and lung cancer.
Section snippets
Materials and methods
Quantitative health impact assessment estimates were derived by linking together: (i) estimates of how proposed policies would affect population exposures; (ii) background mortality rates; and, (iii) concentration–response functions, typically expressed as percentage change in health effect per unit of exposure. This is an established approach when quantifying health impacts mediated by air pollution (O’Connell and Hurley, 2009).
Results
In Spain, the main sectors responsible for emissions of primary fine particles in 2007 and 2014 were road transport and other mobile sources, machinery, non-industrial combustion plants, and combustion in the energy, transformation, and manufacturing industries. The combination of all these accounted for 94% of emissions of this pollutant in 2007. Among these sectors, note should be taken of transport (both road and off-road) with 58% of total fine particle emissions in 2007. By implementing
Discussion
This study reports the mortality impact in Spain expected in 2014, resulting from a mean reduction of 1 µg/m3 in fine particle concentrations. Taking into account 2007 population data, between 8 and 15 all-cause deaths per 100,000 population could be postponed annually by the expected reduction in fine particle levels. For specific subgroups, estimates varied from 10 to 30 deaths for all non-accidental causes, from 1 to 5 for lung cancer, and from 2 to 6 for ischemic heart disease. For each
Conclusions
In conclusion, air pollution constitutes one of the most significant environmental health risks and gives rise to both acute and chronic effects. In view of the fact that exposure to air pollution is a modifiable risk and that, to a great extent, this remains outside the control of the individual, public authorities must assume responsibility for adopting air quality control measures based on available scientific evidence. Compliance with European Directive guideline values should not only be a
Funding sources
This study was funded by a grant from the Spanish Ministry of Agriculture, Food & Environment (058/PC08/3-18.1).
Acknowledgments
Mortality data were supplied by the Spanish National Statistics Institute under a specific confidentiality protocol. The research findings are the responsibility of the authors.
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