| Fig. –1 |
Scheme of ISKOs links to data sources and co-operating systems 2005 |
| Fig. I.1 |
Total emissions of principal pollutants in the Czech Republic between
1990 and 2005 |
| Fig. I.2 |
Changes in fuel structure in REZZO 1, 2004 as compared to 1990 |
| Fig. I.3 |
Fuel consumption in REZZO 3 sources, 1992–2005
|
| Fig. I.4 |
Changes in residential heating, 2005 as compared to 1991 |
| Fig. I.5 |
Changes in REZZO 3 emission quantities at constant structure of flats
and fuels (100 % = average for 2001–2005) |
| Fig. I.6 |
Particulate emission density from 5x5 km squares, 2004 |
| Fig. I.7 |
Sulphur dioxide emission density from 5x5 km squares, 2004 |
| Fig. I.8 |
Nitrogen oxides emission density from 5x5 km squares, 2004 |
| Fig. I.9 |
CO emission density from 5x5 km squares, 2004 |
| Fig. II.1.1 |
Major station networks of ambient air quality monitoring, 2005 |
| Fig. II.1.2 |
Monitoring of principal pollutants in selected organisations –
development |
| Fig. II.4.1 |
Field of the annual concentration of NO2 (3-D image), Prague
agglomeration, 2005 |
| Fig. II.4.2 |
Field of the annual concentration of benzo(a)pyrene (3-D image),
Prague agglomeration, 2005 |
| Fig. II.4.3 |
Field of the annual concentration of NO2 (3-D image), Brno
agglomeration, 2005 |
| Fig. II.4.4 |
Field of the annual concentration of benzo(a)pyrene (3-D image),
Brno agglomeration, 2005 |
| Fig. II.4.5 |
Field of the annual concentration of NO2 (3-D image), Moravian-Silesian
agglomeration, 2005 |
| Fig. II.4.6 |
Field of the annual concentration of benzo(a)pyrene (3-D image),
Moravian-Silesian agglomeration, 2005 |
| Fig. II.4.7 |
Average 24-hour PM10 concentrations, Moravian-Silesian
agglomeration, February 2005 |
| Fig. II.4.8 |
Interdependency between PM10 ambient air pollution and dispersion
meteorological conditions |
| Fig. II.4.9 |
Trends of SO2, PM10 and NO2 annual characteristics in
agglomerations, 1996–2005 |
| Fig. II.4.10 |
4th highest 24-hour concentrations and maximal hourly
concentrations of SO2 in 1996–2005 at selected stations |
| Fig. II.4.11 |
Field of the 4th highest 24-hour concentration of SO2 in 2005 |
| Fig. II.4.12 |
Stations with the highest hourly concentrations of SO2 in 2005 |
| Fig. II.4.13 |
Stations with the highest 24-hour concentrations of SO2 in 2005 |
| Fig. II.4.14 |
36th highest 24-hour concentrations and annual average
concentrations of PM10 in 1996–2005 at selected stations |
| Fig. II.4.15 |
Field of the 36th highest 24-hour concentration of PM10 in 2005 |
| Fig. II.4.16 |
Field of annual average concentration of PM10 in 2005 |
| Fig. II.4.17 |
Stations with the highest exceedence of LV for 24-hour
concentrations of PM10 in 2005 |
| Fig. II.4.18 |
Stations with the highest exceedence of LV for annual
concentrations of PM10 in 2005 |
| Fig. II.4.19 |
Numbers of exceedences of air pollution limit value for the
24-hour concentration of PM10 in 2005 |
| Fig. II.4.20 |
Annual average PM10 concentrations at the stations with the
exceedence of the limit value, 2001–2005 |
| Fig. II.4.21 |
Annual average concentration of PM2.5 at stations in 2005 |
| Fig. II.4.22 |
Average monthly PM2.5/PM10 proportions in 2005 |
| Fig. II.4.23 |
19th highest hourly concentrations and annual average
concentrations of NO2 in 1996–2005 at selected stations |
| Fig. II.4.24 |
Field of annual average concentration of NO2 in 2005 |
| Fig. II.4.25 |
Stations with the highest hourly concentrations of NO2 in 2005 |
| Fig. II.4.26 |
Maximum 8-hour running average concentrations of CO in 1996–2005
at selected stations |
| Fig. II.4.27 |
Stations with the highest values of maximum 8-hour running average
concentrations of CO in 2005 |
| Fig. II.4.28 |
Annual average concentrations of benzene in 1999–2005 at selected
stations |
| Fig. II.4.29 |
Field of annual average concentration of benzene in the ambient
air in 2005 |
| Fig. II.4.30 |
24-hour concentrations at the stations with the highest annual
benzene concentrations in 2005 |
| Fig. II.4.31 |
26th highest values of maximum 8-hour running average of surface
ozone concentrations (three-year average) in 1996–2005 at selected stations |
| Fig. II.4.32 |
Field of the 26th highest maximum daily 8-hour running average of
surface ozone concentration in three-year average, 2003–2005 |
| Fig. II.4.33 |
Numbers of exceedences of the target limit value for the maximum
daily 8-hour running average of surface ozone concentrations in three-year
average, 2003–2005 |
| Fig. II.4.34 |
Stations with the highest values of maximum daily 8-hour running
average concentrations of surface ozone in 2003–2005 |
| Fig. II.4.35 |
Annual average concentrations of lead in the ambient air in
1996–2005 at selected stations |
| Fig. II.4.36 |
1/14-day average concentrations of lead in the ambient air at
selected stations in 2005 |
| Fig. II.4.37 |
Annual average concentrations of cadmium in the ambient air in
1996–2005 at selected stations |
| Fig. II.4.38 |
Field of annual average concentration of cadmium in the ambient
air in 2005 |
| Fig. II.4.39 |
1/14-day average concentrations of cadmium in the ambient air at
selected stations in 2005 |
| Fig. II.4.40 |
Annual average concentrations of arsenic in the ambient air in
1996–2005 at selected stations |
| Fig. II.4.41 |
Field of annual average concentration of arsenic in the ambient
air in 2005 |
| Fig. II.4.42 |
1/14-day average concentrations of arsenic in the ambient air at
selected stations in 2005 |
| Fig. II.4.43 |
Annual average concentrations of nickel in the ambient air in
1996–2005 at selected stations |
| Fig. II.4.44 |
1/14-day average concentrations of nickel in the ambient air at
selected stations in 2005 |
| Fig. II.4.45 |
Annual average concentrations of benzo(a)pyrene in 1997–2005 at
selected stations |
| Fig. II.4.46 |
Field of annual average concentration of benzo(a)pyrene in the
ambient air in 2005 |
| Fig. II.4.47 |
24-hour concentrations at the stations with the highest annual
concentrations of benzo(a)pyrene in 2005 |
| Fig. II.4.48 |
Trends of SO2, PM10, NO2, NOx and O3 annual characteristics in the
Czech Republic, 1996–2005 |
| Fig. II.4.49 |
Annual average concentrations of SO2 in 1996–2005 at selected
stations |
| Fig. II.4.50 |
Winter average concentrations of SO2 in 1996/1997–2005/2006 at
selected stations |
| Fig. II.4.51 |
Field of annual average concentration of SO2 in 2005 |
| Fig. II.4.52 |
Field of average concentration of SO2 in the winter period
2005/2006 |
| Fig. II.4.53 |
24-hour concentrations at the stations with the highest annual
concentrations of SO2 in 2005 |
| Fig. II.4.54 |
24-hour concentrations at the stations with the highest winter
concentrations of SO2 in the winter period 2005/2006 |
| Fig. II.4.55 |
Annual average concentrations of NOx and NO2 in 1996–2005 at
selected stations |
| Fig. II.4.56 |
Field of annual average concentration of NOx in 2005 |
| Fig. II.4.57 |
24-hour concentrations at the stations with the highest annual
concentrations of NOx in 2005 |
| Fig. II.4.58 |
Exposure index AOT40 values of ozone in 1996–2005 at selected
stations, average for 5 years |
| Fig. II.4.59 |
Field of exposure index AOT40 values, average for 5 years,
2001–2005 |
| Fig. II.4.60 |
Stations with the highest exposure index AOT40 values in recent 5
years, 2001–2005 |
| Fig. II.4.61 |
Areas with deteriorated air quality with regard to health
protection limit values, ozone excluded, 2005 |
| Fig. II.4.62 |
Areas with deteriorated air quality with regard to health
protection limit values incl. ozone, 2005 |
| Fig. II.4.63 |
Areas with deteriorated air quality with regard to SO2 and NOx
limit values for the protection of ecosystems/vegetation, 2005 |
| Fig. II.4.64 |
Areas with deteriorated air quality for ecosystems/vegetation,
exceedence of limit value incl. AOT40, 2005 |
| Fig. II.5.1 |
Cessna-TU 206G aeroplane |
| Fig. II.5.2 |
Aircraft measurements of nitrogen dioxide, 1.9.2005,
12:49:00–14:20:00 CET |
| Fig. II.5.3 |
Aircraft measurements of ground-level ozone, 1.9.2005,
12:49:00–14:20:00 CET |
| Fig. II.5.4 |
O3 and NO2 concentration profiles in the direction of prevailing
circulation, 1.9.2005, 12:59:00–14:20:00 CET |
| Fig. II.7.1 |
Average hourly NO2 concentrations at the station Prague 2-Legerova,
1.1.2005–28.2.2005 |
| Fig. II.7.2 |
Course of maximum daily temperatures, their normal and daily total
precipitation at Prague-Libuš station. Occurrence of ozone concentrations
exceeding 180 μg.m-3 on the territory of the Czech Republic, 1.4.2005–30.9.2005 |
| Fig. II.7.3 |
Spatial distribution of maximum hourly concentrations of
ground-level ozone on the territory of the Czech Republic, 29.7.2005 |
| Fig. III.1 |
Station networks monitoring precipitation quality and atmospheric
deposition, 2005 |
| Fig. III.2 |
Fields of annual wet deposition of sulphur (SO42-–S), 2005 |
| Fig. III.3 |
Fields of annual dry deposition of sulphur (SO2–S), 2005 |
| Fig. III.4 |
Fields of annual total deposition of sulphur, 2005 |
| Fig. III.5 |
Fields of annual throughfall deposition of sulphur, 2005 |
| Fig. III.6 |
Fields of annual wet deposition of nitrogen (NO3-–N), 2005 |
| Fig. III.7 |
Fields of annual wet deposition of nitrogen (NH4+–N), 2005 |
| Fig. III.8 |
Fields of annual total wet deposition of nitrogen, 2005 |
| Fig. III.9 |
Fields of annual dry deposition of nitrogen (NOx–N), 2005 |
| Fig. III.10 |
Fields of annual total deposition of nitrogen, 2005 |
| Fig. III.11 |
Fields of annual wet deposition of hydrogen ions, 2005 |
| Fig. III.12 |
Fields of annual dry deposition of hydrogen ions corresponding to
SO2 and NOx deposition, 2005 |
| Fig. III.13 |
Fields of annual total deposition of hydrogen ions, 2005 |
| Fig. III.14 |
Fields of annual wet deposition of fluoride ions, 2005 |
| Fig. III.15 |
Fields of annual wet deposition of chloride ions, 2005 |
| Fig. III.16 |
Fields of annual wet deposition of lead ions, 2005 |
| Fig. III.17 |
Fields of annual dry deposition of lead, 2005 |
| Fig. III.18 |
Fields of annual wet deposition of cadmium ions, 2005 |
| Fig. III.19 |
Fields of annual dry deposition of cadmium, 2005 |
| Fig. III.20 |
Fields of annual wet deposition of nickel ions, 2005 |
| Fig. III.21 |
Annual wet deposition at selected stations between 1991 and 2005,
the Czech Republic |
| Fig. III.22 |
Annual deposition of sulphur (SO42-–S, SO2–S) and oxidated forms of
nitrogen (NO3-–N, NOx–N) and hydrogen in the Czech Republic, 1995–2005 |
