Javier García-Pérez

Dr. Javier García-Pérez

orcid

Research Focus & Metrics

Academic Career Length

20Years (2007-Present)

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

Representative Publications

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1 February 2011 in Environment International
Verified
Journal Article
Closed access
EBElena Boldo
Elena Boldo
CLCristina Linares
Cristina Linares
JLJulio Lumbreras
Julio Lumbreras
Rafael BorgeRafael Borge
Rafael Borge
ASADOLFO NARROS SIERRA
ADOLFO NARROS SIERRA
GLGonzalo López-Abente
Gonzalo López-Abente

1 January 2008 in International Journal of Health Geographics
Verified
Journal Article
Open access
PDF file
JGJavier García-Pérez
Javier García-Pérez
EBElena Boldo
Elena Boldo
Rebeca RamisRebeca Ramis
Rebeca Ramis
EVEnrique Vidal
Enrique Vidal
NANuria Aragonés
Nuria Aragonés
GLGonzalo López-Abente
Gonzalo López-Abente
The European Pollutant Emission Register in Spain (EPER-Spain) is a public inventory of pollutant industries created by decision of the European Union. The location of these industries is geocoded and the first published data correspond to 2001. Publication of these data will allow for quantification of the effect of proximity to one or more such plant on cancer and all-cause mortality observed in nearby towns. However, as errors have been detected in the geocoding of many of the pollutant foci shown in the EPER, it was decided that a validation study should be conducted into the accuracy of these co-ordinates. EPER-Spain geographic co-ordinates were drawn from the European Environment Agency (EEA) server and the Spanish Ministry of the Environment (MOE). The Farm Plot Geographic Information System (Sistema de Información Geográfica de Parcelas Agrícolas) (SIGPAC) enables orthophotos (digitalized aerial images) of any territorial point across Spain to be obtained. Through a search of co-ordinates in the SIGPAC, all the industrial foci (except farms) were located. The quality criteria used to ascertain possible errors in industrial location were high, medium and low quality, where industries were situated at a distance of less than 500 metres, more than 500 metres but less than 1 kilometre, and more than 1 kilometre from their real locations, respectively.

1 October 2012 in Science of The Total Environment
Verified
Journal Article
Closed access
PFPablo Fernández-Navarro
Pablo Fernández-Navarro
JGJavier García-Pérez
Javier García-Pérez
Rebeca RamisRebeca Ramis
Rebeca Ramis
EBElena Boldo
Elena Boldo
GLGonzalo López-Abente
Gonzalo López-Abente

1 July 2015 in Environmental Research
Verified
Journal Article
Closed access
JGJavier García-Pérez
Javier García-Pérez
GLGonzalo López-Abente
Gonzalo López-Abente
DBDiana Gomez Barroso
Diana Gomez Barroso
AMAntonio Morales-Piga
Antonio Morales-Piga
EPElena Pardo-Romaguera
Elena Pardo-Romaguera
Rebeca RamisRebeca Ramis
Rebeca Ramis

1 January 2013 in Environment International
Verified
Journal Article
Open access
JGJavier García-Pérez
Javier García-Pérez
PFPablo Fernández-Navarro
Pablo Fernández-Navarro
APAdela Castelló Pastor
Adela Castelló Pastor
MLMaría Felicitas López-Cima
María Felicitas López-Cima
Rebeca RamisRebeca Ramis
Rebeca Ramis
GLGonzalo López-Abente
Gonzalo López-Abente
Waste treatment plants release toxic emissions into the environment which affect neighboring towns. To investigate whether there might be excess cancer mortality in towns situated in the vicinity of Spanish-based incinerators and installations for the recovery or disposal of hazardous waste, according to the different categories of industrial activity. An ecologic study was designed to examine municipal mortality due to 33 types of cancer, across the period 1997-2006. Population exposure to pollution was estimated on the basis of distance from town of residence to pollution source. Using Besag-York-Mollié (BYM) regression models with Integrated Nested Laplace approximations for Bayesian inference, and Mixed Poisson regression models, we assessed the risk of dying from cancer in a 5-kilometer zone around installations, analyzed the effect of category of industrial activity, and conducted individual analyses within a 50-kilometer radius of each installation. Excess cancer mortality (BYM model: relative risk, 95% credible interval) was detected in the total population residing in the vicinity of these installations as a whole (1.06, 1.04-1.09), and, principally, in the vicinity of incinerators (1.09, 1.01-1.18) and scrap metal/end-of-life vehicle handling facilities, in particular (1.04, 1.00-1.09). Special mention should be made of the results for tumors of the pleura (1.71, 1.34-2.14), stomach (1.18, 1.10-1.27), liver (1.18, 1.06-1.30), kidney (1.14, 1.04-1.23), ovary (1.14, 1.05-1.23), lung (1.10, 1.05-1.15), leukemia (1.10, 1.03-1.17), colon-rectum (1.08, 1.03-1.13) and bladder (1.08, 1.01-1.16) in the vicinity of all such installations. Our results support the hypothesis of a statistically significant increase in the risk of dying from cancer in towns near incinerators and installations for the recovery or disposal of hazardous waste.

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.