| Fig. –1 |
Scheme of ISKO’s links to data sources and co-operating
systems 2007 |
| Fig. I.1 |
Total emissions of basic pollutants in the Czech
Republic between 1990 and 2007 |
| Fig. I.2 |
Changes in types of fuels in the REZZO 1 sources between
1990 and 2006 (shares of heat contained in the fuel) |
| Fig. I.3 |
Fuel consumption in REZZO 3 sources, 1992–2007 |
| Fig. I.4 |
Changes in residential heating – comparison of 1991,
2000 and 2007 |
| Fig. I.5 |
Changes in REZZO 3 emission quantities at constant
structure of flats and fuels (100 % = average for 2001–2005) |
| Fig. I.6 |
Nitrogen oxides emission density from 5x5 km squares,
2006 |
| Fig. I.7 |
Emission density of total suspended particles from 5x5
km squares, 2006 |
| Fig. I.8 |
Sulphur dioxide emission density from 5x5 km squares,
2006 |
| Fig. I.9 |
Carbon monoxide emission density from 5x5 km squares,
2006 |
| Fig. II.1.1 |
Major station networks of ambient air quality
monitoring, 2007 |
| Fig. II.1.2 |
Monitoring of basic pollutants in selected organisations
– development |
| Fig. II.4.1.1 |
PM10 air pollution characteristics for
monitoring stations and basic characteristics of meteorological
conditions in the winter periods (October–March), 2003–2008, Prague
agglomeration |
| Fig. II.4.1.2 |
Annual course of monthly NO2 concentrations
at selected AMS stations, Prague 2007 |
| Fig. II.4.1.3 |
Dependence of average daily PM10
concentrations in Prague on dispersion conditions, 2003–2007 |
| Fig. II.4.1.4 |
The number of days according to the degrees of
dispersion conditions with average daily PM10 concentrations
exceeding 50 μg.m-3 and 100 μg.m-3, 2000–2007 |
| Fig. II.4.1.5 |
Field of the annual concentration of NO2,
Prague agglomeration, 2007 |
| Fig. II.4.1.6 |
Field of the annual concentration of benzo(a)pyrene,
Prague agglomeration, 2007 |
| Fig. II.4.1.7 |
The development of the 36th highest 24-hour
PM10 concentration and average annual temperature, 2000–2007 |
| Fig. II.4.1.8 |
Dependence of PM10 on temperature, 2000–2007 |
| Fig. II.4.1.9 |
Number of exceedances of the 24-hour PM10
limit value in the winter months in relation with the average
temperature of the winter period in Brno-Tuřany locality |
| Fig. II.4.1.10 |
Influence of monthly temperature on the number of 24-hour
PM10 limit value exceedances in the given month in
Mikulov-Sedlec locality, 2004–2005 |
| Fig. II.4.1.11 |
Influence of temperature on PM2.5 and PM10
concentrations, Brno-Tuřany, 2000–2007 |
| Fig. II.4.1.12 |
Influence of temperature on SO2, NO2
and O3 concentrations, Mikulov-Sedlec, 2000–2007 |
| Fig. II.4.1.13 |
Influence of temperature on SO2, NO2
and O3 concentrations, Brno-Kroftova, 2000–2007 |
| Fig. II.4.1.14 |
Influence of temperature on O3 concentrations,
Mikulov-Sedlec, 2000–2007 |
| Fig. II.4.1.15 |
Influence of temperature on benzo(a)pyrene concentration,
Brno-Kroftova, 2004–2007 |
| Fig. II.4.1.16 |
Field of the annual concentration of NO2,
Brno agglomeration, 2007 |
| Fig. II.4.1.17 |
Field of the annual concentration of benzo(a)pyrene,
Brno agglomeration, 2007 |
| Fig. II.4.1.18 |
Average monthly concentrations of PM10, NO2,
SO2, O3 and CO from the stations in the
Ostrava-Karviná area |
| Fig. II.4.1.19 |
Ambient air pollution caused by PM10
particles in the city of Ostrava in winter periods 2001/2002–2007/2008 |
| Fig. II.4.1.20 |
Average meteorological characteristics in winter periods
2001/2002–2007/2008 |
| Fig. II.4.1.21 |
Dependence of average PM10 concentrations on
meteorological characteristics in winter period |
| Fig. II.4.1.22 |
Relative frequencies of the derived daily airflow types |
| Fig. II.4.1.23 |
Average values of meteorological characteristics in
dependence on daily airflow types |
| Fig. II.4.1.24 |
Average daily PM10 concentrations and
relative frequencies of PM10 daily concentrations >50 μg.m-3
in winter period on the days with the respective daily airflow types |
| Fig. II.4.1.25 |
Field of the annual concentration of NO2,
Moravian-Silesian agglomeration, 2007 |
| Fig. II.4.1.26 |
Field of the annual concentration of benzo(a)pyrene,
Moravian-Silesian agglomeration, 2007 |
| Fig. II.4.1.27 |
Annual average PM10 concentration, Ústà nad
Labem Region, 2003–2007 |
| Fig. II.4.1.28 |
36th highest 24-hour PM10
concentration and number of LV exceedances, Ústà nad Labem Region,
2003–2007 |
| Fig. II.4.1.29 |
Number of days per year divided according to four
degrees of dispersion conditions, Krušné hory Mts. area, 2003–2007 |
| Fig. II.4.1.30 |
The number of episodes with deteriorated and
unfavourable conditions lasting four and more days and the total number
of days within these episodes |
| Fig. II.4.1.31 |
Average 24-hour PM10, concentrations,
temperature and dispersion conditions, Ústà nad Labem Region, 2003–2007 |
| Fig. II.4.1.32 |
Trends of SO2, PM10, NO2
and CO annual characteristics in agglomerations, 1996–2007 |
| Fig. II.4.2.1 |
4th highest 24-hour concentrations and
maximum hourly concentrations of SO2 in 1996–2007 at selected
stations |
| Fig. II.4.2.2 |
Field of the 4th highest 24-hour
concentration of SO2 in 2007 |
| Fig. II.4.2.3 |
Stations with the highest hourly concentrations of SO2
in 2007 |
| Fig. II.4.2.4 |
Stations with the highest 24-hour concentrations of SO2
in 2007 |
| Fig. II.4.2.5 |
36th highest 24-hour concentrations and
annual average concentrations of PM10 in 1996–2007 at
selected stations |
| Fig. II.4.2.6 |
Field of the 36th highest 24-hour
concentration of PM10 in 2007 |
| Fig. II.4.2.7 |
Field of annual average concentration of PM10
in 2007 |
| Fig. II.4.2.8 |
Stations with the highest exceedance of LV for 24-hour
concentrations of PM10 in 2007 |
| Fig. II.4.2.9 |
Stations with the highest exceedance of LV for annual
concentrations of PM10 in 2007 |
| Fig. II.4.2.10 |
Numbers of exceedances of air pollution limit value for
the 24-hour concentration of PM10 in 2007 |
| Fig. II.4.2.11 |
Annual average PM10 concentrations at the
stations with the exceedance of the limit value, 2002–2007 |
| Fig. II.4.2.12 |
Annual average concentration of PM2.5 at
stations in 2007 |
| Fig. II.4.2.13 |
Average monthly PM2.5/PM10 ratio
in 2007 |
| Fig. II.4.2.14 |
Stations with the highest exceedance of the proposed LV
for annual concentrations of PM2.5 in 2007 |
| Fig. II.4.2.15 |
Average annual PM10 concentration in Prague
in dependence on dispersion conditions, 2000–2007 |
| Fig. II.4.2.16 |
Spatial distribution of PM10 hourly
concentrations, 23.3. 2007, 0:00–16:00 |
| Fig. II.4.2.17 |
Daily course of PM10 measured on CHMI
automated monitoring stations, 24.3.2007, hourly interval. The graphs
show the maximum measured value and the time of its recording. |
| Fig. II.4.2.18 |
19th highest hourly concentrations and annual
average concentrations of NO2 in 1996–2007 at selected
stations |
| Fig. II.4.2.19 |
Field of annual average concentration of NO2
in 2007 |
| Fig. II.4.2.20 |
Stations with the highest hourly concentrations of NO2
in 2007 |
| Fig. II.4.2.21 |
Stations with the highest exceedance of LV and LV+MT for
annual concentrations of NO2 in 2007 |
| Fig. II.4.2.22 |
Maximum 8-hour running average concentrations of CO in
1996–2007 at selected stations |
| Fig. II.4.2.23 |
Stations with the highest values of maximum 8-hour
running average concentrations of CO in 2007 |
| Fig. II.4.2.24 |
Annual average concentrations of benzene in 1998–2007 at
selected stations |
| Fig. II.4.2.25 |
Field of annual average concentration of benzene in the
ambient air in 2007 |
| Fig. II.4.2.26 |
24-hour concentrations at the stations with the highest
annual benzene concentrations in 2007 |
| Fig. II.4.2.27 |
26th highest values of maximum 8-hour running
average of ground-level ozone concentrations (three-year average) in
1996–2007 at selected stations |
| Fig. II.4.2.28 |
Field of the 26th highest maximum daily 8-hour
running average of ground-level ozone concentrations in three-year
average, 2005–2007 |
| Fig. II.4.2.29 |
Numbers of exceedances of the target value for the
maximum daily 8-hour running average of ground-level ozone
concentrations in three-year average, 2005–2007 |
| Fig. II.4.2.30 |
Stations with the highest values of maximum daily 8-hour
running average concentrations of ground-level ozone in 2005–2007 |
| Fig. II.4.2.31 |
Annual average concentrations of lead in the ambient air
in 1996–2007 at selected stations |
| Fig. II.4.2.32 |
1/14-day average concentrations of lead in the ambient
air in 2007 at selected stations |
| Fig. II.4.2.33 |
Annual average concentrations of cadmium in the ambient
air in 1996–2007 at selected stations |
| Fig. II.4.2.34 |
Field of annual average concentration of cadmium in the
ambient air in 2007 |
| Fig. II.4.2.35 |
1/14-day average concentrations of cadmium in the
ambient air in 2007 at selected stations |
| Fig. II.4.2.36 |
Annual average concentrations of arsenic in the ambient
air in 1996–2007 at selected stations |
| Fig. II.4.2.37 |
Field of annual average concentration of arsenic in the
ambient air in 2007 |
| Fig. II.4.2.38 |
1/14-day average concentrations of arsenic in the
ambient air in 2007 at selected stations |
| Fig. II.4.2.39 |
Annual average concentrations of nickel in the ambient
air in 1996–2007 at selected stations |
| Fig. II.4.2.40 |
1/14-day average concentrations of nickel in the ambient
air in 2007 at selected stations |
| Fig. II.4.2.41 |
Annual average concentrations of benzo(a)pyrene in
1997–2007 at selected stations |
| Fig. II.4.2.42 |
Field of annual average concentration of benzo(a)pyrene
in the ambient air in 2007 |
| Fig. II.4.2.43 |
Month average concentrations of benzo(a)pyrene at
various types of localities, 2004–2007 |
| Fig. II.4.2.44 |
24-hour concentrations at the stations with the highest
annual concentrations of benzo(a)pyrene in 2007 |
| Fig. II.4.2.45 |
Concentrations of benzo(a)pyrene and PM10
particles in individual localities, 2004–2007 |
| Fig. II.4.2.46 |
Trends of SO2, PM10, NO2,
NOx and O3 annual characteristics in the Czech
Republic, 1996–2007 |
| Fig. II.4.2.47 |
Annual average concentrations of SO2 in
1996–2007 at selected rural stations |
| Fig. II.4.2.48 |
Winter average concentrations of SO2 in
1996/1997–2007/2008 at selected rural stations |
| Fig. II.4.2.49 |
Field of annual average concentration of SO2
in 2007 |
| Fig. II.4.2.50 |
Field of average concentration of SO2 in the
winter period 2007/2008 |
| Fig. II.4.2.51 |
24-hour concentrations at the stations with the highest
annual concentrations of SO2 in 2007 |
| Fig. II.4.2.52 |
24-hour concentrations at the stations with the highest
winter concentrations of SO2 in the winter period 2007/2008 |
| Fig. II.4.2.53 |
Annual average concentrations of NOx and NO2
in 1996–2007 at selected stations |
| Fig. II.4.2.54 |
Field of annual average concentration of NOx
in 2007 |
| Fig. II.4.2.55 |
24-hour concentrations at the stations with the highest
annual concentrations of NOx in 2007 |
| Fig. II.4.2.56 |
Exposure index AOT40 values of ozone in 1996–2007 at
selected stations, average for 5 years |
| Fig. II.4.2.57 |
Field of exposure index AOT40 values, average for 5
years, 2003–2007 |
| Fig. II.4.2.58 |
Stations with the highest exposure index AOT40 values in
recent 5 years, 2003–2007 |
| Fig. II.4.2.59 |
Areas with deteriorated air quality with regard to
health protection limit values, 2007 |
| Fig. II.4.2.60 |
Areas with deteriorated air quality with regard to
health protection target values, ground-level ozone excluded, 2007 |
| Fig. II.4.2.61 |
Areas with deteriorated air quality with regard to
health protection target values, incl. ground-level ozone, 2007 |
| Fig. II.4.2.62 |
Areas with deteriorated air quality with regard to
ecosystems/vegetation protection limit values in national parks and
protected landscape areas, ground-level ozone excluded, 2007 |
| Fig. II.4.2.63 |
Areas with deteriorated air quality with regard to
ecosystems/vegetation protection limit values in national parks and
protected landscape areas, including ground-level ozone, 2007 |
| Fig. II.5.1 |
Course of daily average air temperatures and the long-term
normal, Prague-Libuš, 1.1.–28.2.2007 |
| Fig. II.5.2 |
Average hourly NO2 concentrations at the
station Prague 2-Legerova, 1.1.–28.2.2007 |
| Fig. II.5.3 |
Average hourly NO2 concentrations at the
station Prague 2-Legerova, 1.11.–31.12.2007 |
| Fig. II.5.4 |
Course of maximum daily air temperatures, their normal
and daily sums of precipitation at the station Prague-Libuš. Occurrence
of ozone concentrations exceeding 180 μg.m-3 in the territory
of the Czech Republic, 1.4.–30.9.2007 |
| Fig. II.5.5 |
Spatial distribution of maximum daily hourly
concentrations of ground-level ozone in the territory of the Czech
Republic, 14.7.–22.7.2007 |
| Fig. III.1 |
Station networks monitoring atmospheric precipitation
quality and atmospheric deposition, 2007 |
| Fig. III.2 |
Fields of annual wet deposition of sulphur (SO42-
- S), 2007 |
| Fig. III.3 |
Fields of annual dry deposition of sulphur (SO2
- S), 2007 |
| Fig. III.4 |
Fields of annual total deposition of sulphur, 2007 |
| Fig. III.5 |
Fields of annual throughfall deposition of sulphur, 2007 |
| Fig. III.6 |
Fields of annual wet deposition of nitrogen (NO3-
- N), 2007 |
| Fig. III.7 |
Fields of annual wet deposition of nitrogen (NH4+
- N), 2007 |
| Fig. III.8 |
Fields of annual total wet deposition of nitrogen, 2007 |
| Fig. III.9 |
Fields of annual dry deposition of nitrogen (NOx
- N), 2007 |
| Fig. III.10 |
Fields of annual total deposition of nitrogen, 2007 |
| Fig. III.11 |
Fields of annual wet deposition of hydrogen ions, 2007 |
| Fig. III.12 |
Fields of annual dry deposition of hydrogen ions
corresponding to SO2 and NOx deposition, 2007 |
| Fig. III.13 |
Fields of annual total deposition of hydrogen ions, 2007 |
| Fig. III.14 |
Fields of annual wet deposition of fluoride ions, 2007 |
| Fig. III.15 |
Fields of annual wet deposition of chloride ions, 2007 |
| Fig. III.16 |
Fields of annual wet deposition of lead ions, 2007 |
| Fig. III.17 |
Fields of annual dry deposition of lead, 2007 |
| Fig. III.18 |
Fields of annual wet deposition of cadmium ions, 2007 |
| Fig. III.19 |
Fields of annual dry deposition of cadmium, 2007 |
| Fig. III.20 |
Fields of annual wet deposition of nickel ions, 2007 |
| Fig. III.21 |
The development of annual deposition of sulphur (SO42–S,
SO2–S) and oxidated forms of nitrogen (NO3-–N,
NOx–N) and hydrogen in the Czech Republic, 1995–2007 |
| Fig. III.22 |
The development of the ratio of nitrate/sulphate
concentrations in atmospheric deposition (expressed as μeq. l-1)
at the CHMI stations, 1998–2007 |
| Fig. III.23 |
The development of annual wet deposition at selected
stations in 1991–2007, Czech Republic |
