AIR POLLUTION IN THE CZECH REPUBLIC IN 2003
Czech Hydrometeorological Institute - Air Quality Protection Division





 LIST OF FIGURES

Fig. –1 Scheme of ISKOs links to data sources and co-operating systems
Fig. 1.1 Total emissions of principal pollutants in the Czech Republic between 1990 and 2003
Fig. 1.2 Fuel consumption in REZZO 3 sources, 1992–2003
Fig. 1.3 Changes in residential heating in 2003 as compared to 1991
Fig. 1.4 Particulate emission density from 5x5 km squares, 2002
Fig. 1.5 Sulphur dioxide emission density from 5x5 km squares, 2002
Fig. 1.6 Nitrogen oxide emission density from 5x5 km squares, 2002
Fig. 1.7 CO emission density from 5x5 km squares, 2002
Fig. 2.1.1 Major station networks of ambient air quality monitoring, 2003
Fig. 2.1.2 Monitoring of principal pollutants in selected organisations – development
Fig. 2.2.1 4th highest 24-hour concentrations and annual average concentrations of SO2 in 1992–2003 at selected stations
Fig. 2.2.2 Field of the 4th highest 24-hour concentration of SO2 in 2003
Fig. 2.2.3 Stations with the highest hourly concentrations of SO2 in 2003
Fig. 2.2.4 Stations with the highest 24-hour concentrations of SO2 in 2003
Fig. 2.2.5 36th highest 24-hour concentrations and annual average concentrations of PM10 in 1994–2003 at selected stations
Fig. 2.2.6 Field of the 36th highest 24-hour concentration of PM10 in 2003
Fig. 2.2.7 Field of annual average concentration of PM10 in 2003
Fig. 2.2.8 Stations with the highest exceedence of LV+MT for 24-hour concentrations of PM10 in 2003
Fig. 2.2.9 19th highest hourly concentrations and annual average concentrations of NO2 in 1992–2003 at selected stations
Fig. 2.2.10 Field of annual average concentration of NO2 in 2003
Fig. 2.2.11 Stations with the highest hourly concentrations of NO2 in 2003
Fig. 2.2.12 Annual average concentrations of lead in the ambient air in 1992–2003 at selected stations
Fig. 2.2.13 7/14-day average concentrations of lead in the ambient air at selected stations in 2003
Fig. 2.2.14 Maximum 8-hour moving average concentrations of CO in 1994–2003 at selected stations
Fig. 2.2.15 Stations with the highest values of maximum 8-hour moving average concentrations of CO in 2003
Fig. 2.2.16 Annual average concentrations of benzene in 1999–2003 at selected stations
Fig. 2.2.17 24-hour concentrations at the stations with the highest annual benzene concentrations in 2003
Fig. 2.2.18 26th highest values of maximum 8-hour moving average of ozone concentrations (three-year average) in 1992–2003 at selected stations
Fig. 2.2.19 Field of the 26th highest maximum daily 8-hour moving average of ozone concentration in three-year average, 2001–2003
Fig. 2.2.20 Stations with the highest values of maximum daily 8-hour moving average concentrations of ozone in 2001-2003
Fig. 2.2.21 Annual average concentrations of cadmium in the ambient air in 1992–2003 at selected stations
Fig. 2.2.22 Field of annual average concentration of cadmium in the ambient air in 2003
Fig. 2.2.23 1/14-day average concentrations of cadmium in the ambient air at selected stations in 2003
Fig. 2.2.24 Annual average concentrations of arsenic in the ambient air in 1992–2003 at selected stations
Fig. 2.2.25 Field of annual average concentration of arsenic in the ambient air in 2003
Fig. 2.2.26 1/14-day average concentrations of arsenic in the ambient air at selected stations in 2003
Fig. 2.2.27 Annual average concentrations of nickel in the ambient air in 1992–2003 at selected stations
Fig. 2.2.28 1/14-day average concentrations of nickel in the ambient air at selected stations in 2003
Fig. 2.2.29 Annual average concentrations of benzo(a)pyrene in 1997–2003 at selected stations
Fig. 2.2.30 Field of annual average concentration of benzo(a)pyrene in the ambient air in 2003
Fig. 2.2.31 24-hour concentrations at the stations with the highest annual concentrations of benzo(a)pyrene in 2003
Fig. 2.2.32 Trends of SO2, PM10, NO2 and O3 annual characteristics in the Czech Republic, 1994–2003
Fig. 2.2.33 Trends of SO2, PM10 and NO2 annual characteristics in agglomerations, 1994–2003
Fig. 2.2.34 Areas/administrative units with deteriorated air quality with regard to health protection limit values, ozone excluded, 2003
Fig. 2.2.35 Areas/administrative units with deteriorated air quality with regard to health protection limit values incl. ozone, 2003
Fig. 2.2.36 Winter average concentrations of SO2 in 1992/1993–2003/2004 at selected stations
Fig. 2.2.37 Field of average concentration of SO2 in the winter period 2003/2004
Fig. 2.2.38 Annual average concentrations of NOx in 1992–2003 at selected stations
Fig. 2.2.39 Field of annual average concentration of NOx in 2003
Fig. 2.2.40 AOT40 values of ozone in 1995–2003 at selected stations
Fig. 2.2.41 Field of AOT40 value of ozone, average of 5 years 1999 - 2003
Fig. 2.2.42 Stations with the highest AOT40 values in recent 5 years, 1999–2003
Fig. 2.2.43 Areas with deteriorated air quality with regard to SO2 and NOx limit values for the protection of ecosystems/vegetation, 2003
Fig. 2.2.44   Areas with deteriorated air quality for ecosystems/vegetation, exceedence of limit value AOT40, 2003
Fig. 2.3.1 Course of maximum daily temperatures, their long-term average and daily total precipitation at Prague-Libuš station. Occurrence of ozone concentrations exceeding 180 μg.m-3 on the territory of the Czech Republic. 1. 4. 2003–30. 9. 2003
Fig. 2.3.2 Maximum hourly concentrations of ground-level ozone on the territory of the Czech Republic, 12 August 2003
Fig. 2.3.3 Spatial distribution of maximum hourly concentrations of ground-level ozone on the territory of the Czech Republic, 12 August 2003
Fig. 2.3.4 Maximum hourly concentrations of ground-level ozone in Prague, 12 August 2003
Fig. 2.3.5 Maximum hourly concentrations of ground-level ozone on the territory of the Czech Republic, 13 August 2003
Fig. 2.3.6 Spatial distribution of maximum hourly concentrations of ground-level ozone on the territory of the Czech Republic, 13 August 2003
Fig. 2.3.7 Maximum hourly concentrations of ground-level ozone in Prague, 13 August 2003
Fig. 2.3.8 Maximum hourly concentrations of ground-level ozone on the territory of the Czech Republic, 14 August 2003
Fig. 2.3.9 Spatial distribution of maximum hourly concentrations of ground-level ozone on the territory of the Czech Republic, 14 August 2003
Fig. 2.3.10 Maximum hourly concentrations of ground-level ozone in Prague, 14 August 2003
Fig. 2.3.11 Analysis of air temperatures at the level of 850 hPa, 10–15 August 2003
Fig. 3.1 Station networks monitoring precipitation quality and atmospheric deposition, 2003
Fig. 3.2 Fields of annual wet deposition of sulphur (SO42- - S), 2003
Fig. 3.3 Fields of annual dry deposition of sulphur (SO2 - S), 2003
Fig. 3.4 Fields of annual total deposition of sulphur, 2003
Fig. 3.5 Fields of annual throughfall deposition of sulphur, 2003
Fig. 3.6 Fields of annual wet deposition of nitrogen (NO3- - N), 2003
Fig. 3.7 Fields of annual wet deposition of nitrogen (NH4+ - N), 2003
Fig. 3.8 Fields of annual total wet deposition of nitrogen, 2003
Fig. 3.9 Fields of annual dry deposition of nitrogen (NOx - N), 2003
Fig. 3.10 Fields of annual total deposition of nitrogen, 2003
Fig. 3.11 Fields of annual wet deposition of hydrogen ions, 2003
Fig. 3.12 Fields of annual dry deposition of hydrogen ions corresponding to SO2 and NOx deposition, 2003
Fig. 3.13 Fields of annual total deposition of hydrogen ions, 2003
Fig. 3.14 Fields of annual wet deposition of fluoride ions, 2003
Fig. 3.15 Fields of annual wet deposition of chloride ions, 2003
Fig. 3.16 Fields of annual wet deposition of lead ions, 2003
Fig. 3.17 Fields of annual dry deposition of lead, 2003
Fig. 3.18 Fields of annual wet deposition of cadmium ions, 2003
Fig. 3.19 Fields of annual dry deposition of cadmium, 2003
Fig. 3.20 Fields of annual wet deposition of nickel ions, 2003
Fig. 3.21 Annual wet deposition at selected stations between 1991 and 2003, the Czech Republic
Fig. 3.22 Annual deposition of sulphur and oxidated forms of nitrogen in the Czech Republic, 1995–2003