Author:
Hoffmann Leona,Gilardi Lorenza,Schmitz Marie-Therese,Erbertseder Thilo,Bittner Michael,Wüst Sabine,Schmid Matthias,Rittweger Jörn
Abstract
AbstractWhen analyzing health data in relation to environmental stressors, it is crucial to identify which variables to include in the statistical model to exclude dependencies among the variables. Four meteorological parameters: temperature, ultraviolet radiation, precipitation, and vapor pressure and four outdoor air pollution parameters: ozone ($$\text{O}_3$$
O
3
), nitrogen dioxide ($$\text{NO}_2$$
NO
2
), particulate matter ($$PM_{2.5}$$
P
M
2.5
, $$PM_{10}$$
P
M
10
) were studied on a daily basis for Baden-Württemberg (Germany). This federal state covers urban and rural compartments including mountainous and river areas. A temporal and spatial analysis of the internal relationships was performed among the variables using (a) cross-correlations, both on the grand ensemble of data as well as within subsets, and (b) the Local Indications of Spatial Association (LISA) method. Meteorological and air pollution variables were strongly correlated within and among themselves in time and space. We found a strong interaction between nitrogen dioxide and ozone, with correlation coefficients varying over time. The coefficients ranged from negative correlations in January (−0.84), April (−0.47), and October (−0.54) to a positive correlation in July (0.45). The cross-correlation plot showed a noticeable change in the correlation direction for $$\text{O}_3$$
O
3
and $$\text{NO}_2$$
NO
2
. Spatially, $$\text{NO}_2$$
NO
2
, $$PM_{2.5}$$
P
M
2.5
, and $$PM_{10}$$
P
M
10
concentrations were significantly higher in urban than rural regions. For $$\text{O}_3$$
O
3
, this effect was reversed. A LISA analysis confirmed distinct hot and cold spots of environmental stressors. This work examined and quantified the spatio-temporal relationship between air pollution and meteorological conditions and recommended which variables to prioritize for future health impact analyses. The results found are in line with the underlying physico-chemical atmospheric processes. It also identified postal code areas with dominant environmental stressors for further studies.
Funder
Deutsche Forschungsgesellschaft
Deutsches Zentrum für Luft- und Raumfahrt e. V. (DLR)
Publisher
Springer Science and Business Media LLC
Reference62 articles.
1. Jacob, D. J. & Winner, D. A. Effect of climate change on air quality. Atmos. Environ.https://doi.org/10.1016/j.atmosenv.2008.09.051 (2009).
2. Doherty, R. M., Heal, M. R. & O’Connor, F. M. Climate change impacts on human health over Europe through its effect on air quality. Environ. Health. 16(1), 33–44. https://doi.org/10.1186/s12940-017-0325-2 (2017).
3. World Health Organization (WHO). WHO Global Air Quality Guidelines: Particulate Matter (PM2.5 and PM10), Ozone, Nitrogen Dioxide, Sulfur Dioxide and Carbon Monoxide. (World Health Organization, 2021). https://www.who.int/publications/i/item/9789240034228.
4. World Health Organization (WHO). Air Quality Guidelines: Global Update 2005: Particulate Matter, Ozone, Nitrogen Dioxide, and Sulfur Dioxide. (World Health Organization, 2006). WHO/SDE/PHE/OEH/06.02. https://www.who.int/publications/i/item/WHO-SDE-PHE-OEH-06.02.
5. The European Parliament and the Council of the European Union. Directive 2008/50/EC of the European Parliament and of the Council of 21 May 2008 on ambient air quality and cleaner air for Europe. J. Eur. Union. (2008).
Cited by
1 articles.
订阅此论文施引文献
订阅此论文施引文献,注册后可以免费订阅5篇论文的施引文献,订阅后可以查看论文全部施引文献