Estimates of population exposure to atmospheric pollution and health-related externalities in a real city: The impact of spatial resolution on the accuracy of results

被引:31
作者
Santiago, J. L. [1 ]
Rivas, E. [1 ]
Gamarra, A. R. [2 ]
Vivanco, M. G. [1 ]
Buccolieri, R. [3 ]
Martilli, A. [1 ]
Lechon, Y. [2 ]
Martin, F. [1 ]
机构
[1] CIEMAT, Atmospher Pollut Div, Environm Dept, Madrid, Spain
[2] CIEMAT, DOE, Madrid, Spain
[3] Univ Salento, Dipartimento Sci & Tecnol Biol Ambientali, Lecce, Italy
关键词
Computational Fluid Dynamic (CFD) modelling; City scale; NO2 health-related externalities; Population exposure; Urban air quality; AIR-QUALITY; PARTICULATE MATTER; PERSONAL EXPOSURE; TREES; REPRESENTATIVENESS; NEIGHBORHOOD; MORTALITY; CHILDREN; PM2.5; PM10;
D O I
10.1016/j.scitotenv.2021.152062
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Health impacts of atmospheric pollution is an important issue in urban environments. Its magnitude depends on population exposure which have been frequently estimated by considering different approaches relating pollutant concentration and population exposed to it. However, the uncertainties due to the spatial resolution of the model used to estimate the pollutant concentration or due to the lack of representativeness of urban air quality monitoring station (AQMS) have not been evaluated in detail. In this context, NO2 annual average concentration at pedestrian level in the whole city of Pamplona (Spain) modelled at high spatial resolution (~1 m) by Computational Fluid Dynamic (CFD) simulations is used to estimate the total population exposure and health-related externalities by using different approaches. Air pollutant concentration and population are aggregated at different spatial resolutions ranging from a horizontal grid cell size of 100 m x 100 m to a coarser resolution where the whole city is covered by only one cell (6 km x 5 km). In addition, concentrations at AQMS locations are also extracted to assess the representativeness of those AQMS. The case with a spatial resolution of 100 m x 100 m for both pollutant-concentration distribution and population data is used as a reference (Base case) and compared with those obtained with the other approaches. This study indicates that the spatial resolution of concentration and population distribution in the city should be 1 km x 1 km or finer to obtain appropriate estimates of total population exposure (underestimations < 13%) and health-related externalities (underestimations < 37%). For the cases with coarser resolutions, a strong underestimation of total population exposure (> 31%) and health-related externalities (> 76%) was found. On the other hand, the use of AQMS concentrations can induce important errors due to the limited spatial representativeness, in particular in terms of population exposure.
引用
收藏
页数:16
相关论文
共 68 条
[1]   Air Pollution and the Microvasculature: A Cross-Sectional Assessment of In Vivo Retinal Images in the Population-Based Multi-Ethnic Study of Atherosclerosis (MESA) [J].
Adar, Sara D. ;
Klein, Ronald ;
Klein, Barbara E. K. ;
Szpiro, Adam A. ;
Cotch, Mary Frances ;
Wong, Tien Y. ;
O'Neill, Marie S. ;
Shrager, Sandi ;
Barr, R. Graham ;
Siscovick, David S. ;
Daviglus, Martha L. ;
Sampson, Paul D. ;
Kaufman, Joel D. .
PLOS MEDICINE, 2010, 7 (11)
[2]  
Amann M., 2017, Costs, Benefits and Economic Impacts of the EU Clean Air Strategy and Their Implications on Innovation and Competitiveness
[3]   CFD modelling of the aerodynamic effect of trees on urban air pollution dispersion [J].
Amorim, J. H. ;
Rodrigues, V. ;
Tavares, R. ;
Valente, J. ;
Borrego, C. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2013, 461 :541-551
[4]  
Anderson HR., 2007, Quantitative Systematic Review of Short Term Associations Between Ambient Air Pollution (Particulate Matter, Ozone, Nitrogen Dioxide, Sulphur Dioxide And Carbon Monoxide), and Mortality and Morbidity
[5]  
[Anonymous], 2016, ISBN, V978, P88, DOI DOI 10.2337/DB15-0956
[6]   Personal exposure of children to air pollution [J].
Ashmore, M. R. ;
Dimitroulopoulou, C. .
ATMOSPHERIC ENVIRONMENT, 2009, 43 (01) :128-141
[7]   CALIOPE-Urban v1.0: coupling R-LINE with a mesoscale air quality modelling system for urban air quality forecasts over Barcelona city (Spain) [J].
Benavides, Jaime ;
Snyder, Michelle ;
Guevara, Marc ;
Soret, Albert ;
Perez Garcia-Pando, Carlos ;
Amato, Fulvio ;
Querol, Xavier ;
Jorba, Oriol .
GEOSCIENTIFIC MODEL DEVELOPMENT, 2019, 12 (07) :2811-2835
[8]   Air quality modeling and mortality impact of fine particles reduction policies in Spain [J].
Boldo, Elena ;
Linares, Cristina ;
Aragones, Nuria ;
Lumbreras, Julio ;
Borge, Rafael ;
de la Paz, David ;
Perez-Gomez, Beatriz ;
Fernandez-Navarro, Pablo ;
Garcia-Perez, Javier ;
Pollan, Marina ;
Ramis, Rebeca ;
Moreno, Teresa ;
Karanasiou, Angeliki ;
Lopez-Abente, Gonzalo .
ENVIRONMENTAL RESEARCH, 2014, 128 :15-26
[9]   Application of a short term air quality action plan in Madrid (Spain) under a high-pollution episode - Part II: Assessment from multi-scale modelling [J].
Borge, Rafael ;
Luis Santiago, Jose ;
de la Paz, David ;
Martin, Fernando ;
Domingo, Jessica ;
Valdes, Cristina ;
Sanchez, Beatriz ;
Rivas, Esther ;
Teresa Rozas, Ma ;
Lazaro, Sonia ;
Perez, Javier ;
Fernandez, Alvaro .
SCIENCE OF THE TOTAL ENVIRONMENT, 2018, 635 :1574-1584
[10]   Assessment of microscale spatio-temporal variation of air pollution at an urban hotspot in Madrid (Spain) through an extensive field campaign [J].
Borge, Rafael ;
Narros, Adolfo ;
Artinano, Begona ;
Yague, Carlos ;
Javier Gomez-Moreno, Francisco ;
de la Paz, David ;
Roman-Cascon, Carlos ;
Diaz, Elias ;
Maqueda, Gregorio ;
Sastre, Mariano ;
Quaassdorff, Christina ;
Dimitroulopoulou, Chrysanthi ;
Vardoulakis, Sotiris .
ATMOSPHERIC ENVIRONMENT, 2016, 140 :432-445