LIST OF FIGURES
Fig. 1 | Areas with exceeding of the health protection limit values for selected groups of pollutants, 2014 |
Fig. I.1 | Major station networks of ambient air quality monitoring, 2014 |
Fig. I.2 | The zones and agglomerations for ambient air quality assessment and evaluation of ambient air pollution level according to the Act No. 201/2012 Coll. On Clear Air Protection, as amended |
Fig. II.1 | The development of total emissions, 1990–2001 |
Fig. II.2 | The development of total emissions, 2002–2013 |
Fig. II.3 | The output of basic industrial products, 1990–2013 |
Fig. II.4 | Fuel consumption in REZZO 3 sources, 1990–2014 |
Fig. III.1 | Annual heating seasons in the CR expressed in degree days (D21) and their average for the period 1984–2013 |
Fig. III.2 | Annual course of degree days in the territory of the CR in the heating season 2014 (I–V, IX–XII) in comparison with the average for 1984–2013 |
Fig. III.3 | Temperature, dispersion conditions, and concentrations of PM10 and O3 in the agglomeration of Ostrava/Karviná/Frýdek-Místek, 2014 |
Fig. III.4 | Annual course of the occurrence of dispersion conditions in the CR and agglomerations, 2014 |
Fig. IV.1.1 | Field of the 36th highest 24-hour concentration of PM10, 2014 |
Fig. IV.1.2 | Field of annual average concentration of PM10, 2014 |
Fig. IV.1.3 | Numbers of exceedances of the limit value for 24-hour concentration of PM10, 2014 |
Fig. IV.1.4 | Field of annual average concentration of PM2.5, 2014 |
Fig. IV.1.5 | 36th highest 24-hour concentrations and annual average concentrations of PM10 at selected stations with UB, SUB, T and I classification, 2004–2014 |
Fig. IV.1.6 | 36th highest 24-hour concentrations and annual average concentrations of PM10 at selected rural (R) stations, 2004–2014 |
Fig. IV.1.7 | Annual average concentrations of PM2.5 in the ambient air at selected stations, 2004–2014 |
Fig. IV.1.8 | Share of localities with the exceedance of the limit value for 24-hour concentration of PM10 and annual average concentrations of PM10 and PM2.5, 2000–2014 |
Fig. IV.1.9 | Five-year average of annual average concentrations of PM10, 2010–2014 |
Fig. IV.1.10 | Five-year average of annual average concentrations of PM2.5, 2010–2014 |
Fig. IV.1.11 | Annual course of average monthly concentrations of PM10 (averages for the given type of station), 2014 |
Fig. IV.1.12 | Annual course of average monthly concentrations of PM2.5 (averages for the given type of station), 2014 |
Fig. IV.1.13 | Average monthly PM2.5/PM10 ratio, 2014 |
Fig. IV.1.14 | Stations with the highest exceedance of LV for 24-hour concentrations of PM10, 2014 |
Fig. IV.1.15 | Trends of PM10 annual characteristics in the Czech Republic, 2000–2014 |
Fig. IV.1.16 | Trends of PM2.5 annual characteristics in the Czech Republic, 2005–2014 |
Fig. IV.1.17 | Trends of selected characteristics of PM10 (index, year 2000 = 100), 2000–2014 and PM2.5 (index, year 2005 = 100), 2005–2014 |
Fig. IV.1.18 | Total emissions of PM10 sorted out by NFR sectors, 2013 |
Fig. IV.1.19 | The development of PM10 total emissions, 2007–2013 |
Fig. IV.1.20 | Total emissions of PM2.5 sorted out by NFR sectors, 2013 |
Fig. IV.1.21 | The development of PM2.5 total emissions, 2007–2013 |
Fig. IV.1.22 | PM10 emission density from 5x5 km squares, 2013 |
Fig. IV.1.23 | PM2.5 emission density from 5x5 km squares, 2013 |
Fig. IV.1.24 | Numerical size distribution of aerosol particles (median, 25th and 75th percentile, 5th and 95th percentile) measured at the Košetice observatory over a period of five years (Zíková et al. 2014) |
Fig. IV.1.25 | Numerical size distribution of aerosol particles (median, 25th and 75th percentile, 5th and 95th percentile) measured at the station Ústí nad Labem-město for 7 size categories over the period of 2012–2014 |
Fig. IV.1.26 | Average monthly concentrations of EC and OC at the Košetice observatory, 2009–2014 |
Fig. IV.1.27 | Monthly variation of average concentrations of EC and OC at the Košetice observatory, 2009–2014 |
Fig. IV.1.28 | Annual progression of concentrations of BC in PM1 measured at the Ústí nad Labem-centrum station, 2013–2014 |
Fig. IV.2.1 | Field of annual average concentration of benzo[a]pyrene, 2014 |
Fig. IV.2.2 | Annual average concentrations of benzo[a]pyrene in the ambient air at selected stations, 2004–2014 |
Fig. IV.2.3 | Five-year average of annual average concentrations of benzo[a]pyrene, 2010–2014 |
Fig. IV.2.4 | Trends of benzo[a]pyrene annual characteristics in the Czech Republic, 2006–2014 |
Fig. IV.2.5 | Annual course of average monthly concentrations of benzo[a]pyrene (averages for the given type of station), 2014 |
Fig. IV.2.6 | Average monthly concentrations of benzo[a]pyrene and PM10 particles at individual localities in winter months, 2014 |
Fig. IV.2.7 | Concentrations of benzo[a]pyrene and PM10 particles at individual localities in winter months, 2010–2014 |
Fig. IV.2.8 | 24-hour concentrations at the stations with the highest annual concentrations of benzo[a]pyrene, 2014 |
Fig. IV.2.9 | Total emissions of benzo[a]pyrene sorted out by NFR sectors, 2013 |
Fig. IV.2.10 | The development of benzo[a]pyrene total emissions, 2007–2013 |
Fig. IV.2.11 | Benzo[a]pyrene emission density from 5x5 km squares, 2013 |
Fig. IV.3.1 | Field of annual average concentration of NO2, 2014 |
Fig. IV.3.2 | Five-year average of annual average concentrations of NO2, 2010–2014 |
Fig. IV.3.3 | Field of annual average concentration of NOx , 2014 |
Fig. IV.3.4 | Annual course of average monthly concentrations of NO2 (averages for the given type of station), 2014 |
Fig. IV.3.5 | Trends of NO2 and NOx annual characteristics in the Czech Republic, 2000–2014 |
Fig. IV.3.6 | Trends of selected characteristics of NO2 and NOx (index, year 2000 = 100), 2000–2014 |
Fig. IV.3.7 | Stations with the highest hourly concentrations of NO2, 2014 |
Fig. IV.3.8 | 24-hour concentrations at the stations with the highest annual concentrations of NOx , 2014 |
Fig. IV.3.9 | 19th highest hourly concentrations and annual average concentrations of NO2 at selected stations, 2004–2014 |
Fig. IV.3.10 | Annual average concentrations of NOx at selected rural stations, 2004–2014 |
Fig. IV.3.11 | Total emissions of NOx sorted out by NFR sectors, 2013 |
Fig. IV.3.12 | The development of NOx total emissions, 2007–2013 |
Fig. IV.3.13 | Nitrogen oxide emission density from 5x5 km squares, 2013 |
Fig. IV.4.1 | Field of the 26th highest maximum daily 8-hour running average of ground-level ozone concentration in three-year average, 2012–2014 |
Fig. IV.4.2 | 26th highest values of maximum daily 8-hour running average of ground-level ozone concentrations (three-year average) at selected stations, 2004–2014 |
Fig. IV.4.3 | Annual course of average monthly concentrations of max. 8-hour running average of O3 (averages for the given type of station), 2014 |
Fig. IV.4.4 | Field of AOT40 exposure index values, average of 5 years, 2010–2014 |
Fig. IV.4.5 | Numbers of exceedances of the limit value for the maximum daily 8-hour running average of ground-level ozone concentrations in three-year average, 2012–2014 |
Fig. IV.4.6 | Trends of O3 annual characteristics in the Czech Republic, 2000–2014 |
Fig. IV.4.7 | Trends of selected characteristics of O3 (index, year 2000 = 100), 2000–2014 |
Fig. IV.4.8 | Exposure index AOT40 values at selected stations, average of 5 years 2004–2014 |
Fig. IV.4.9 | Annual exposure index AOT40 values at selected stations, 2010–2014 |
Fig. IV.5.1 | Field of annual average concentration of benzene, 2014 |
Fig. IV.5.2 | Annual average concentrations of benzene at selected stations, 2004–2014 |
Fig. IV.5.3 | Five-year average of annual average concentrations of benzene, 2010–2014 |
Fig. IV.5.4 | Trends of benzene annual characteristics in the Czech Republic, 2005–2014 |
Fig. IV.5.5 | 24-hour concentrations at the stations with the highest annual benzene concentrations, 2014 |
Fig. IV.6.1 | Field of annual average concentration of cadmium in the ambient air, 2014 |
Fig. IV.6.2 | Field of annual average concentration of arsenic in the ambient air, 2014 |
Fig. IV.6.3 | Five-year average of annual average concentrations of cadmium, 2010–2014 |
Fig. IV.6.4 | Five-year average of annual average concentrations of arsenic, 2010–2014 |
Fig. IV.6.5 | Annual average concentrations of lead in the ambient air at selected stations, 2004–2014 |
Fig. IV.6.6 | Annual average concentrations of cadmium in the ambient air at selected stations, 2004–2014 |
Fig. IV.6.7 | Annual average concentrations of arsenic in the ambient air at selected stations, 2004–2014 |
Fig. IV.6.8 | Annual average concentrations of nickel in the ambient air at selected stations, 2004–2014 |
Fig. IV.6.9 | Trends of heavy metals annual characteristics in the Czech Republic, 2006–2014 |
Fig. IV.6.10 | Total emissions of arsenic sorted out by NFR sectors, 2013 |
Fig. IV.6.11 | The development of arsenic total emissions, 2007–2013 |
Fig. IV.6.12 | Total emissions of nickel sorted out by NFR sectors, 2013 |
Fig. IV.6.13 | The development of nickel total emissions, 2007–2013 |
Fig. IV.6.14 | Total emissions of cadmium sorted out by NFR sectors, 2013 |
Fig. IV.6.15 | The development of cadmium total emissions, 2007–2013 |
Fig. IV.6.16 | Total emissions of lead sorted out by NFR sectors, 2013 |
Fig. IV.6.17 | The development of lead total emissions, 2007–2013 |
Fig. IV.6.18 | Arsenic emission density from 5x5 km squares, 2013 |
Fig. IV.6.19 | Nickel emission density from 5x5 km squares, 2013 |
Fig. IV.6.20 | Cadmium emission density from 5x5 km squares, 2013 |
Fig. IV.6.21 | Lead emission density from 5x5 km squares, 2013 |
Fig. IV.7.1 | Field of the 4th highest 24-hour concentration of SO2, 2014 |
Fig. IV.7.2 | 4th highest 24-hour concentrations and 25th highest hourly concentrations of SO2 at selected stations, 2004–2014 |
Fig. IV.7.3 | Trends of SO2 annual characteristics in the Czech Republic, 2000–2014 |
Fig. IV.7.4 | Trends of selected characteristics of SO2 (index, year 2000 = 100), 2000–2014 |
Fig. IV.7.5 | Field of annual average concentration of SO2, 2014 |
Fig. IV.7.6 | Field of average concentration of SO2 in the winter period 2014/2015 |
Fig. IV.7.7 | Annual average concentrations of SO2 at selected rural stations, 2004–2014 |
Fig. IV.7.8 | Winter average concentrations of SO2 at selected rural stations, 2004/2005–2014/2015 |
Fig. IV.7.9 | Total emissions of SO2 sorted out by NFR sectors, 2013 |
Fig. IV.7.10 | The development of SO2 total emissions, 2007–2013 |
Fig. IV.7.11 | Sulphur dioxide emission density from 5x5 km squares, 2013 |
Fig. IV.8.1 | Maximum daily 8-hour running average concentrations of CO at selected stations, 2004–2014 |
Fig. IV.8.2 | Total emissions of CO sorted out by NFR sectors, 2013 |
Fig. IV.8.3 | The development of CO total emissions, 2007–2013 |
Fig. IV.8.4 | Carbon moNOx ide emission density from 5x5 km squares, 2013 |
Fig. IV.9.1.1 | Annual course of average monthly concentrations of VOC, 2014 |
Fig. IV.9.1.2 | Total emissions of VOC sorted out by NFR sectors, 2013 |
Fig. IV.9.1.3 | The development of VOC total emissions, 2007–2013 |
Fig. IV.9.2.1 | Total emissions of NH3 sorted out by NFR sectors, 2013 |
Fig. IV.9.2.2 | The development of NH3 total emissions, 2007–2013 |
Fig. IV.9.3.1 | Total emissions of mercury sorted out by NFR sectors, 2013 |
Fig. IV.9.3.2 | The development of mercury total emissions, 2007–2013 |
Fig. V.1 | Trends of SO2, NO2, CO (2000–2014) and benzene (2005–2014) annual characteristics at urban and suburban stations in agglomerations |
Fig. V.2 | Trends of PM10 (2000–2014), PM2.5 (2005–2014) and benzo[a]pyrene (2006–2014) annual characteristics at urban and suburban stations in agglomerations |
Fig. V.1.1 | Number of exceedances of 24-hour PM10 limit value and the 36th highest 24-hour concentration PM10 at individual types of stations, agglomeration of Prague, 2006–2014 |
Fig. V.1.2 | Number of days with concentrations of PM10 > 50 µg.m-3 in individual months, incl. total number of exceedances, agglomeration of Prague, 2014 |
Fig. V.1.3 | Average annual PM2.5 concentrations, agglomeration of Prague, 2004–2014 |
Fig. V.1.4 | Numbers of exceedances of the hourly limit value for NO2 at the traffic station Prague 2-Legerova (hot spot), agglomeration of Prague, 2003–2014 |
Fig. V.1.5 | Average annual benzo[a]pyrene concentrations, agglomeration of Prague, 2000–2014 |
Fig. V.1.6 | Numbers of exceedances of the limit value of O3 in the average for three years, agglomeration of Prague, 2006–2014 |
Fig. V.1.7 | Field of the annual concentration of NO2, agglomeration of Prague, 2014 |
Fig. V.1.8 | Field of the 36th highest 24-hour concentration of PM10, agglomeration of Prague, 2014 |
Fig. V.1.9 | Emissions of selected pollutants listed according to REZZO, agglomeration of Prague |
Fig. V.2.1 | Average annual PM10 concentrations in selected localities and at individual types of stations, agglomeration of Brno, 2006–2014 |
Fig. V.2.2 | Average monthly PM10 concentrations, Kuchařovice, 2005–2014 |
Fig. V.2.3 | Average annual PM2.5 concentrations, agglomeration of Brno, 2006–2014 |
Fig. V.2.4 | Number of exceedances of 24-hour PM10 limit value in selected localities and 36th highest 24-hour concentration of PM10 at individual types of stations, agglomeration of Brno, 2006–2014 |
Fig. V.2.5 | Number of days with concentrations of PM10 > 50 µg.m-3 in individual months, incl. total number of exceedances, agglomeration of Brno, 2014 |
Fig. V.2.6 | Average monthly NO2 and PM10 concentrations, locality Brno-Úvoz (hot spot) |
Fig. V.2.7 | Average annual NO2 concentrations in selected localities and at individual types of stations, agglomeration of Brno, 2006–2014 |
Fig. V.2.8 | Average annual benzo[a]pyrene concentrations, agglomeration of Brno, 2006–2014 |
Fig. V.2.9 | Field of the annual concentration of NO2, agglomeration of Brno, 2014 |
Fig. V.2.10 | Field of the 36th highest 24-hour concentration of PM10, agglomeration of Brno, 2014 |
Fig. V.3.1 | Average annual PM10 concentrations in selected localities and at individual types of stations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2006–2014 |
Fig. V.3.2 | Average annual PM2.5 concentrations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2004–2014 |
Fig. V.3.3 | Number of days with concentrations of PM10 > 50 µg.m-3 in individual months, incl. total number of exceedances, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2014 |
Fig. V.3.4 | Number of exceedances of 24-hour limit value for PM10 in selected localities and the 36th highest 24-hour concentrations of PM10 at individual types of stations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2006–2014 |
Fig. V.3.5 | Average annual NO2 concentrations in selected localities and at individual types of stations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2006–2014 |
Fig. V.3.6 | Average annual benzo[a]pyrene concentrations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2000–2014 |
Fig. V.3.7 | Number of exceedances of the limit value of O3 in the average for three years, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2006–2014 |
Fig. V.3.8 | Field of the annual concentration of NO2, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2014 |
Fig. V.3.9 | Field of the 36th highest 24-hour concentration of PM10, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2014 |
Fig. V.4.1 | Relative representation of values of the air quality index calculated based on hourly concentrations of NO2, PM10 and O3 at urban and suburban automated stations, 2014 |
Fig. VI.1 | SWRS areas and representative stations for PM10 |
Fig. VI.2 | SWRS areas and representative stations for O3 |
Fig. VI.3 | SWRS areas and representative stations for SO2 |
Fig. VI.4 | SWRS areas and representative stations for NO2 |
Fig. VI.5 | Smog situations and regulations for PM10 in the SWRS areas in which at least one smog situation was announced, 2014 |
Fig. VI.6 | The episode with high ozone concentrations at the station Prague-Libuš, June 2014 |
Fig. VI.7 | The episodes with high PM10 concentrations in the agglomeration of Ostrava/Karviná/Frýdek-Místek without Třinec area, December 2014 |
Fig. VII.1 | Areas with exceeding of the health protection limit values, ground-level ozone excluded, 2014 |
Fig. VII.2 | Areas with exceeding of the health protection limit values, incl. ground-level ozone, 2014 |
Fig. VII.3 | Limit value exceedances in the Czech Republic, % of the area, 2006–2014 |
Fig. VII.4 | Areas with exceeding of the ecosystems/vegetation protection limit values in national parks and protected landscape areas, ground-level ozone excluded, 2014 |
Fig. VII.5 | Areas with exceeding of the ecosystems/vegetation protection limit values in national parks and protected landscape areas, including ground-level ozone, 2014 |
Fig. VIII.1 | Development of concentrations of PM10, O3 and NO2 recalculated according to the number of urban inhabitants in 28 member states of the European Union, 2003–2012 |
Fig. VIII.2 | Development of emissions in 28 member states of the European Union, 2003–2012 |
Fig. VIII.3 | Annual average concentration of PM2.5 in Europe, 2012 |
Fig. VIII.4 | Annual average concentration of benzo[a]pyrene in Europe, 2012 |
Fig. VIII.5 | Annual average concentration of NO2 in Europe, 2012 |
Fig. VIII.6 | The 26th highest maximum daily 8-hour average of O3 concentration in Europe, 2012 |
Fig. IX.1 | Station networks monitoring atmospheric precipitation quality and atmospheric deposition, 2014 |
Fig. IX.2 | Fields of annual wet deposition of sulphur (SO42- - S), 2014 |
Fig. IX.3 | Fields of annual dry deposition of sulphur (SO2 - S), 2014 |
Fig. IX.4 | Fields of annual total deposition of sulphur, 2014 |
Fig. IX.5 | Fields of annual throughfall deposition of sulphur, 2014 |
Fig. IX.6 | Fields of annual wet deposition of nitrogen (NO3- - N), 2014 |
Fig. IX.7 | Fields of annual wet deposition of nitrogen (NH4+ - N), 2014 |
Fig. IX.8 | Fields of annual total wet deposition of nitrogen, 2014 |
Fig. IX.9 | Fields of annual dry deposition of nitrogen (NOx - N), 2014 |
Fig. IX.10 | Fields of annual total deposition of nitrogen, 2014 |
Fig. IX.11 | Fields of annual wet deposition of hydrogen ions, 2014 |
Fig. IX.12 | Fields of annual dry deposition of hydrogen ions corresponding to SO2 and NOx deposition, 2014 |
Fig. IX.13 | Fields of annual total deposition of hydrogen ions, 2014 |
Fig. IX.14 | Fields of annual wet deposition of chloride ions, 2014 |
Fig. IX.15 | Fields of annual wet deposition of lead ions, 2014 |
Fig. IX.16 | Fields of annual dry deposition of lead, 2014 |
Fig. IX.17 | Fields of annual wet deposition of cadmium ions, 2014 |
Fig. IX.18 | Fields of annual dry deposition of cadmium, 2014 |
Fig. IX.19 | Fields of annual wet deposition of nickel ions, 2014 |
Fig. IX.20 | The development of annual deposition of sulphur (SO42- - S, SO2 - S), oxidated forms of nitrogen (NO3- - N, NOx - N) and hydrogen in the Czech republic, 1995–2014 |
Fig. IX.21 | The development of the ratio of nitrate/sulphate concentrations in atmospheric deposition (expressed as µeq. l-1) at the CHMI stations, 1998–2014 |
Fig. IX.22 | The development of annual wet deposition at selected stations, 1991–2014 |
Fig. X.1 | Emissions of carbon dioxide structured by sectors, 1990–2013 |
Fig. X.2 | Emissions of methane structured by sectors, 1990–2013 |
Fig. X.3 | Emissions of nitrous oxide structured by sectors, 1990–2013 |
Fig. X.4 | Emissions of F-gases, 1995–2013 |
Fig. X.5 | Carbon dioxide emissions from the plants registered in EU ETS, 2005–2013 |
Fig. XI.1 | Ties of the AQIS to data sources and co-operating systems, 2014 |
Fig. XI.2 | Monitoring of basic pollutants in selected organisations – development |
Fig. XII.1 | Diagram showing the variogram parameters and the fitted spherical function |
Annex III | |
Fig. 1 | Concentration wind roses expressing the dependence of average hourly concentrations of PM10 on wind direction and speed, locality Polom, 2014 |
Fig. 2 | Seasonal concentration wind roses expressing the dependence of average hourly concentrations of PM10 on wind direction and speed, locality Polom, 2014 |
Fig. 3 | Number of exceedances of the hourly PM10 concentration of 50 µg.m-3 depending on the time of day, locality Polom, 2014 |
Fig. 4 | Number of exceedances of the hourly PM10 concentration of 50 µg.m-3 depending on the day of the week, locality Polom, 2014 |
Fig. 5 | Number of exceedances of the hourly PM10 concentration of 50 µg.m-3 depending on the time of day, locality Krupka, winter period 2013/X–2014/III |
Fig. 6 | Number of exceedances of the hourly PM10 concentration of 50 µg.m-3 depending on the day of the week, locality Krupka, winter period 2013/X–2014/III |
Fig. 7 | Concentration wind roses expressing the dependence of average hourly concentrations of PM10 on wind direction and speed, locality Krupka, winter period 2013/X–2014/III |
Fig. 8 | Concentration wind roses expressing the dependence of average hourly concentrations of PM10 on wind direction and speed, locality Krupka, winter period 2014/X–2015/III |
Annex IV | |
Fig. 1 | Field of the highest 24-hour concentration of PM10, 2014 (WHO) |
Fig. 2 | Field of the highest 24-hour concentration of PM2.5, 2014 (WHO) |
Fig. 3 | Field of the highest hourly concentration of NO2, 2014 (WHO) |
Fig. 4 | Field of the highest maximum daily 8-hour running average of ground-level ozone concentration, 2014 (WHO) |
Fig. 5 | Field of the highest 24-hour concentration of SO2, 2014 (WHO) |