Elsevier

Environmental Research

Volume 128, January 2014, Pages 15-26
Environmental Research

Air quality modeling and mortality impact of fine particles reduction policies in Spain

https://doi.org/10.1016/j.envres.2013.10.009Get rights and content

Highlights

  • Effective implementation of air quality policies would decline fine particles levels.

  • It was estimated a mean overall reduction in fine particles of 1 µg/m3 by 2014 in Spain.

  • A range from 2365 to 4163 all-cause deaths could be postponed annually in Spain.

  • Air quality control plans would lead to notable health-related benefits.

Abstract

Background

In recent years, Spain has implemented a number of air quality control measures that are expected to lead to a future reduction in fine particle concentrations and an ensuing positive impact on public health.

Objectives

We aimed to assess the impact on mortality attributable to a reduction in fine particle levels in Spain in 2014 in relation to the estimated level for 2007.

Methods

To estimate exposure, we constructed fine particle distribution models for Spain for 2007 (reference scenario) and 2014 (projected scenario) with a spatial resolution of 16×16 km2. In a second step, we used the concentration–response functions proposed by cohort studies carried out in Europe (European Study of Cohorts for Air Pollution Effects and Rome longitudinal cohort) and North America (American Cancer Society cohort, Harvard Six Cities study and Canadian national cohort) to calculate the number of attributable annual deaths corresponding to all causes, all non-accidental causes, ischemic heart disease and lung cancer among persons aged over 25 years (2005–2007 mortality rate data). We examined the effect of the Spanish demographic shift in our analysis using 2007 and 2012 population figures.

Results

Our model suggested that there would be a mean overall reduction in fine particle levels of 1 µg/m3 by 2014. 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. The expected burden of preventable mortality would be even higher in the future due to the Spanish population growth. Taking into account the population older than 30 years in 2012, the absolute mortality impact estimate would increase approximately by 18%.

Conclusions

Effective implementation of air quality measures in Spain, in a scenario with a short-term projection, would amount to an appreciable decline in fine particle concentrations, and this, in turn, would lead to notable health-related benefits. Recent European cohort studies strengthen the evidence of an association between long-term exposure to fine particles and health effects, and could enhance the health impact quantification in Europe. Air quality models can contribute to improved assessment of air pollution health impact estimates, particularly in study areas without air pollution monitoring data.

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 AtmosféricaSERCA) 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.

References (57)

  • N. Pérez et al.

    Partitioning of major and trace components in PM10-PM2.5_PM1 at an urban site in Southern Europe

    Atmos. Environ.

    (2008)
  • O. Raaschou-Nielsen et al.

    Air pollution and lung cancer incidence in 17 European cohorts: prospective analyses from the European Study of Cohorts for Air Pollution Effects (ESCAPE)

    Lancet Oncol.

    (2013)
  • Abt Associates Inc. 2010a. BenMAP. User's Manual. Appendices. Prepared for Office of Air Quality Planning and...
  • Abt Associates Inc. 2010b. BenMAP. User's manual. Prepared for Office of Air Quality Planning and Standards, US EPA....
  • Z.J. Andersen et al.

    Diabetes incidence and long-term exposure to air pollution: a cohort study

    Diabetes Care

    (2012)
  • S.C. Anenberg et al.

    An estimate of the global burden of anthropogenic ozone and fine particulate matter on premature human mortality using atmospheric modeling

    Environ. Health Perspect.

    (2010)
  • F. Ballester et al.

    Reducing ambient levels of fine particulates could substantially improve health: a mortality impact assessment for 26 European cities

    J. Epidemiol. Community Health

    (2008)
  • R. Beelen et al.

    Long-term effects of traffic-related air pollution on mortality in a Dutch cohort (NLCS-AIR study)

    Environ. Health Perspect.

    (2008)
  • V. Bertomeu et al.

    Situación de la enfermedad cardiovascular en España. Del riesgo a la enfermedad

    Rev. Esp. Cardiol.

    (2008)
  • K. Bhaskaran et al.

    Cardiovascular consequences of air pollution: what are the mechanisms?

    Heart

    (2011)
  • R.D. Brook et al.

    Particulate matter air pollution and cardiovascular disease: an update to the scientific statement from the American Heart Association

    Circulation

    (2010)
  • B. Brunekreef et al.

    Effects of long-term exposure to traffic-related air pollution on respiratory and cardiovascular mortality in the Netherlands: the NLCS-AIR study

    Res. Rep. Health Eff. Inst.

    (2009)
  • D. Byun et al.

    Review of the governing equations, computational algorithms, and other components of the models-3 community multiscale air quality (CMAQ) modeling system

    Appl. Mech. Rev.

    (2006)
  • D. Byun et al.

    Science algorithms of the EPA models-3 community multiscale air quality (CMAQ) modeling system [microform]

  • G. Cesaroni et al.

    Long-term exposure to urban air pollution and mortality in a cohort of more than a million adults in Rome

    Environ. Health Perspect.

    (2013)
  • D.L. Crouse et al.

    Risk of non-accidental and cardiovascular mortality in relation to long-term exposure to low concentrations of fine particulate matter: a Canadian National-level cohort study

    Environ. Health Perspect.

    (2012)
  • M. Cusack et al.

    Trends of particulate matter (PM2.5) and chemical composition at a regional background site in the Western Mediterranean over the last nine years (2002–2010)

    Atmos. Chem. Phys. Discuss.

    (2012)
  • Eurostat, 2013. Europe indicators. Online at: 〈http://epp.eurostat.ec.europa.eu/〉. (accessed...
  • Cited by (57)

    • Spatially-structured human mortality modelling using air pollutants with a compositional approach

      2022, Science of the Total Environment
      Citation Excerpt :

      The regression coefficients inverse-transformed were the same for each county. Interestingly, the coefficient related to PM2.5 has the most important influence (0.67) over the mortality data modelling; this result has been widely studied in Spain by Boldo et al. (2014). The number of human deaths in Spain increased with the age-group level, as shown in Fig. 5.

    • Linking air quality, health, and economic effect models for use in air pollution epidemiology studies with uncertain factors

      2021, Atmospheric Pollution Research
      Citation Excerpt :

      There are different chemical transport models that could be used in this kind of studies, as for example the Community Multiscale Air Quality Modeling System (CMAQ) (Binkowski and Shankar, 1995; Jun and Stein, 2004; Byun and Schere, 2006; Holmes et al., 2014; Mai et al., 2016; Abel et al., 2018; Wu et al., 2019), Comprehensive Air Quality Model with Extensions (Pepe et al., 2016), and Weather Research and Forecast model coupled with Chemistry (Grell et al., 2005) were developed to assess transmission and associated metabolism (de Almeida Albuquerque et al., 2012; Vara-Vela et al., 2016). In recent years, the application of models to determine regional public health impacts has received special attention (Boldo et al., 2014; Russell et al., 2014; Ding et al., 2016; Li et al., 2019). In this context, air quality modelling, particularly for PM10 and PM2.5, is of interest because of the connection of PM to people's health.

    • Estimates of pedestrian exposure to atmospheric pollution using high-resolution modelling in a real traffic hot-spot

      2021, Science of the Total Environment
      Citation Excerpt :

      For example, when mesoscale Chemical-Transport Models (CTM) are used, the grid resolution can range from 1 km to several tens of km, which is usually a better spatial resolution than the one obtained interpolating only air quality monitors, particularly, in urban environments because of the small spatial representativeness of urban AQMS. These pollutant concentration maps can be combined with population data (such as population density) with a similar spatial resolution to carry out health impact assessment studies (Boldo et al., 2014; Izquierdo et al., 2020). However, in urban areas, the spatial variability of air pollutant concentration is very strong as a result of the complex air flows due to the buildings or other obstacles.

    View all citing articles on Scopus
    View full text