4 research outputs found

    Additional file 1: of Air pollution modelling for birth cohorts: a time-space regression model

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    Figure S1. Spatial distribution of the BECO (rural) and AFU (urban) measurement locations in the canton of Bern, displayed on background NO2 from the 2007 dispersion model. Figure S2. NO2 levels measured in a sample of urban monitoring sites during the year 2007. Figure S3. Internal validation Bland-Altman plot of predicted and measured values in the rural region (top) and urban area (bottom) in the log scale. Figure S4. Bland-Altman plot for external validation in Ī¼g/m3 (rural or urban model without intercept, corrected for backyard measurements). Table S1. Potential predictors of NO2. Table S2. Variance Inflation Factors (VIF) of main predictors in the rural and urban model. Table S3. Kappa statistics for External validation ā€“ measured vs estimated concentration in quartiles. (DOCX 1047 kb

    Evaluation of Land Use Regression Models for NO<sub>2</sub> and Particulate Matter in 20 European Study Areas: The ESCAPE Project

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    Land use regression models (LUR) frequently use leave-one-out-cross-validation (LOOCV) to assess model fit, but recent studies suggested that this may overestimate predictive ability in independent data sets. Our aim was to evaluate LUR models for nitrogen dioxide (NO<sub>2)</sub> and particulate matter (PM) components exploiting the high correlation between concentrations of PM metrics and NO<sub>2</sub>. LUR models have been developed for NO<sub>2</sub>, PM<sub>2.5</sub> absorbance, and copper (Cu) in PM<sub>10</sub> based on 20 sites in each of the 20 study areas of the ESCAPE project. Models were evaluated with LOOCV and ā€œhold-out evaluation (HEV)ā€ using the correlation of predicted NO<sub>2</sub> or PM concentrations with measured NO<sub>2</sub> concentrations at the 20 additional NO<sub>2</sub> sites in each area. For NO<sub>2</sub>, PM<sub>2.5</sub> absorbance and PM<sub>10</sub> Cu, the median LOOCV <i>R</i><sup>2</sup>s were 0.83, 0.81, and 0.76 whereas the median HEV <i>R</i><sup>2</sup> were 0.52, 0.44, and 0.40. There was a positive association between the LOOCV <i>R</i><sup>2</sup> and HEV <i>R</i><sup>2</sup> for PM<sub>2.5</sub> absorbance and PM<sub>10</sub> Cu. Our results confirm that the predictive ability of LUR models based on relatively small training sets is overestimated by the LOOCV <i>R</i><sup>2</sup>s. Nevertheless, in most areas LUR models still explained a substantial fraction of the variation of concentrations measured at independent sites

    Development of Land Use Regression Models for PM<sub>2.5</sub>, PM<sub>2.5</sub> Absorbance, PM<sub>10</sub> and PM<sub>coarse</sub> in 20 European Study Areas; Results of the ESCAPE Project

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    Land Use Regression (LUR) models have been used increasingly for modeling small-scale spatial variation in air pollution concentrations and estimating individual exposure for participants of cohort studies. Within the ESCAPE project, concentrations of PM<sub>2.5</sub>, PM<sub>2.5</sub> absorbance, PM<sub>10</sub>, and PM<sub>coarse</sub> were measured in 20 European study areas at 20 sites per area. GIS-derived predictor variables (e.g., traffic intensity, population, and land-use) were evaluated to model spatial variation of annual average concentrations for each study area. The median model explained variance (<i>R</i><sup>2</sup>) was 71% for PM<sub>2.5</sub> (range across study areas 35ā€“94%). Model <i>R</i><sup>2</sup> was higher for PM<sub>2.5</sub> absorbance (median 89%, range 56ā€“97%) and lower for PM<sub>coarse</sub> (median 68%, range 32ā€“ 81%). Models included between two and five predictor variables, with various traffic indicators as the most common predictors. Lower <i>R</i><sup>2</sup> was related to small concentration variability or limited availability of predictor variables, especially traffic intensity. Cross validation <i>R</i><sup>2</sup> results were on average 8ā€“11% lower than model <i>R</i><sup>2</sup>. Careful selection of monitoring sites, examination of influential observations and skewed variable distributions were essential for developing stable LUR models. The final LUR models are used to estimate air pollution concentrations at the home addresses of participants in the health studies involved in ESCAPE

    Development of Land Use Regression Models for Particle Composition in Twenty Study Areas in Europe

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    Land Use Regression (LUR) models have been used to describe and model spatial variability of annual mean concentrations of traffic related pollutants such as nitrogen dioxide (NO<sub>2</sub>), nitrogen oxides (NO<sub><i>x</i></sub>) and particulate matter (PM). No models have yet been published of elemental composition. As part of the ESCAPE project, we measured the elemental composition in both the PM<sub>10</sub> and PM<sub>2.5</sub> fraction sizes at 20 sites in each of 20 study areas across Europe. LUR models for eight a priori selected elements (copper (Cu), iron (Fe), potassium (K), nickel (Ni), sulfur (S), silicon (Si), vanadium (V), and zinc (Zn)) were developed. Good models were developed for Cu, Fe, and Zn in both fractions (PM<sub>10</sub> and PM<sub>2.5</sub>) explaining on average between 67 and 79% of the concentration variance (<i>R</i><sup>2</sup>) with a large variability between areas. Traffic variables were the dominant predictors, reflecting nontailpipe emissions. Models for V and S in the PM<sub>10</sub> and PM<sub>2.5</sub> fractions and Si, Ni, and K in the PM<sub>10</sub> fraction performed moderately with <i>R</i><sup>2</sup> ranging from 50 to 61%. Si, NI, and K models for PM<sub>2.5</sub> performed poorest with <i>R</i><sup>2</sup> under 50%. The LUR models are used to estimate exposures to elemental composition in the health studies involved in ESCAPE
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