Cristina Linares

Dr. Cristina Linares

Department of Epidemiology and Biostatistics, National School of Public Health, Carlos III National Institute of Health (Instituto Salud Carlos III/ISCIII), Madrid, Spain

Research Focus & Metrics

Academic Career Length

15Years (2012-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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29 October 2022 in Environmental Research
Verified
Journal Article
Closed access
IMIsidro Miron
Isidro Miron
Cristina LinaresCristina Linares
Cristina Linares
Julio DiazJulio Diaz
Julio Diaz

1 February 2015 in Environmental Research
Verified
Journal Article
Closed access
Aurelio TobiasAurelio Tobias
Aurelio Tobias
ARAlberto Recio
Alberto Recio
Julio DiazJulio Diaz
Julio Diaz
Cristina LinaresCristina Linares
Cristina Linares

1 February 2016 in Environmental Research
Verified
Journal Article
Closed access
VAVirginia Arroyo
Virginia Arroyo
Julio DiazJulio Diaz
Julio Diaz
COCristina Ortiz
Cristina Ortiz
RCRocío Carmona
Rocío Carmona
MSMarc Sáez
Marc Sáez
Cristina LinaresCristina Linares
Cristina Linares

1 November 2016 in Environmental Pollution
Verified
Journal Article
Closed access
VAVirginia Arroyo
Virginia Arroyo
Julio DiazJulio Diaz
Julio Diaz
RCRocío Carmona
Rocío Carmona
COCristina Ortiz
Cristina Ortiz
Cristina LinaresCristina Linares
Cristina Linares

8 March 2012 in Environmental Health
Verified
Journal Article
Open access
PDF file
Julio DiazJulio Diaz
Julio Diaz
Aurelio TobiasAurelio Tobias
Aurelio Tobias
Cristina LinaresCristina Linares
Cristina Linares
Background: Saharan dust intrusions are a common phenomenon in the Madrid atmosphere, leading induce exceedances of the 50 μg/m3- EU 24 h standard for PM10. Methods: We investigated the effects of exposure to PM10 between January 2003 and December 2005 in Madrid (Spain) on daily case-specific mortality; changes of effects between Saharan and non-Saharan dust days were assessed using a time-stratified case-crossover design. Results: Saharan dust affected 20% of days in the city of Madrid. Mean concentration of PM10 was higher during dust days (47.7 μg/m3) than non-dust days (31.4 μg/m3). The rise of mortality per 10 μg/m3 PM10 concentration were always largely for Saharan dust-days. When stratifying by season risks of PM10, at lag 1, during Saharan dust days were stronger for respiratory causes during cold season (IR% = 3.34% (95% CI: 0.36, 6.41) versus 2.87% (95% CI: 1.30, 4.47)) while for circulatory causes effects were stronger during warm season (IR% = 4.19% (95% CI: 1.34, 7.13) versus 2.65% (95% CI: 0.12, 5.23)). No effects were found for cerebrovascular causes. Conclusions: We found evidence of strongest effects of particulate matter during Saharan dust days, providing a suggestion of effect modification, even though interaction terms were not statistically significant. Further investigation is needed to understand the mechanism by which Saharan dust increases mortality.

1 January 2014 in Environmental Research
Verified
Journal Article
Open access
EBElena Boldo
Elena Boldo
Cristina LinaresCristina Linares
Cristina Linares
NANuria Aragonés
Nuria Aragonés
JLJulio Lumbreras
Julio Lumbreras
Rafael BorgeRafael Borge
Rafael Borge
GLGonzalo López-Abente
Gonzalo López-Abente
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. 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. To estimate exposure, we constructed fine particle distribution models for Spain for 2007 (reference scenario) and 2014 (projected scenario) with a spatial resolution of 16×16km(2). 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. Our model suggested that there would be a mean overall reduction in fine particle levels of 1µg/m(3) 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%. 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.