6 research outputs found
Nominally significant gene-environment interactions by outcome and exposure.
<p>Genes are sorted in ascending order of interaction p-value within outcome-exposure strata.</p>a<p>significant after Bonferroni-correction for testing 152 genes (α = .00033).</p>b<p>marginally significant after Bonferroni-correction for testing 152 genes (α = .00033).</p
Distribution of interaction p-values across genes mapping to pathways with weak interaction signals.
<p>P-values of interaction on the gene-level are given on a minus log<sub>10</sub> scale (y-axis), i.e. higher bars represent smaller interaction p-values. (A) Genes of the mitochondrial dysfunction pathway interacting with PM10 and packyears exposure between surveys on FEV<sub>1</sub>/FVC decline. (B) Genes of the methane metabolism pathway interacting with PM10 and packyears exposure between surveys on FEF<sub>25–75</sub> decline. (C) Genes of the apoptosis signaling pathway interacting with PM10 and packyears exposure between surveys on FEV<sub>1</sub> decline.</p
Mapping of candidate oxidative-stress genes to molecular pathways of interest.
<p>Mapping of candidate oxidative-stress genes to molecular pathways of interest.</p
Distribution of main characteristics by smoking status at follow-up and PM<sub>10</sub> exposure during follow-up (N = 650<sup>1</sup>).
1<p>restricted to sample with complete data on all three lung function parameters. Regarding FEV<sub>1</sub>, sample size with complete covariate data would be n = 669.</p>2<p>means for age and lung function values, medians for pack years exposures.</p
Effect estimates of the strongest interacting SNP from each nominally significant gene on FEV<sub>1</sub>/FVC decline (n = 650).
<p>SNP-estimates are based on an additive model. Beta-estimates represent percentages of decline in FEV<sub>1</sub>/FVC over 11 years per effect allele and/or for an exposure contrast of one interquartile range (IQR). All estimates are taken from the same interaction model. Positive values mean an attenuation, and negative ones an acceleration of FEV<sub>1</sub>/FVC decline. Rows are sorted according to ascending interaction p-values.</p>*<p>significant after Bonferroni correction for testing 12679 SNPs (α = 3.9×10E-6).</p><p>gen: genotyped SNP; imp: imputed SNP; All1: allele 1 (effect allele); All2: allele 2 (baseline allele); FreqAll1: frequency of allele 1.</p
Evaluation of Land Use Regression Models for NO<sub>2</sub> and Particulate Matter in 20 European Study Areas: The ESCAPE Project
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 “hold-out evaluation (HEV)” 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