LIST OF FIGURES

Fig. 1 Areas with exceeding of the health protection limit values for one or more pollutants
Fig. I.1 Major station networks of ambient air quality monitoring, 2013
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 Clean Air Protection, as amended
Fig. II.1 The development of total emissions, 1990–2001
Fig. II.2 The development of total emissions, 2002–2012
Fig. II.3 The output of basic industrial products, 1990–2012 (Source: ČSÚ)
Fig. II.4 Fuel consumption in REZZO 3 sources, 1990–2013
Fig. III.1 Annual heating seasons in the CR expressed in degree days (D21) and their average for the period 1983–2012. Td is the average daily temperature in the heating days.
Fig. III.2 Daily course of the occurrence of dispersion conditions (%) at the station Prague-Libuš in the years 2004–2012
Fig. III.3 Annual course of the occurrence of dispersion conditions (%) at the station Prague-Libuš in the years 2004–2012
Fig. III.4 Annual course of degree days in the territory of the CR in the heating season 2013 (I–V, IX–XII) in comparison with the average for 1983–2012
Fig. III.5 Annual course of the occurrence of dispersion conditions at the stations Prague-Libuš and Prostějov in the year 2013
Fig. III.6 The episode with high ozone concentrations at the station Prague-Libuš, 1. 7.–31. 8. 2013
Fig. III.7 The episodes with high PM10 concentrations in the agglomeration of Ostrava/Karviná/Frýdek-Místek without Třinec area in January and February 2013
Fig. III.8 Temperature, dispersion conditions, types of weather situations and concentrations of PM10 and O3 in the agglomeration of Ostrava/Karviná/Frýdek-Místek without Třinec area in the year 2013
Fig. IV.1.1 Field of the 36th highest 24-hour concentration of PM10 in 2013
Fig. IV.1.2 Field of annual average concentration of PM10 in roce 2013
Fig. IV.1.3 Numbers of exceedances of the limit value for 24-hour concentration of PM10 in 2013
Fig. IV.1.4 Annual course of average monthly concentrations of PM10 (averages for the given type of station), 2013
Fig. IV.1.5 Stations with the highest exceedance of LV for 24-hour concentrations of PM10 in 2013
Fig. IV.1.6 Stations with the highest exceedance of LV for annual concentrations of PM10 in 2013
Fig. IV.1.7 Field of annual average concentration of PM2.5 in 2013
Fig. IV.1.8 Average monthly PM2.5/PM10 ratio in 2013
Fig. IV.1.9 Stations with the highest exceedance of LV for annual concentrations of PM2.5 in 2013
Fig. IV.1.10 36th highest 24-hour concentrations and annual average concentrations of PM10 in 2003–2013 at selected stations with UB, SUB, I and T classification
Fig. IV.1.11 36th highest 24-hour concentrations and annual average concentrations of PM10 in 2003–2013 at selected rural (R) stations
Fig. IV.1.12 Annual average PM10 concentrations at the stations with the exceedance of the limit value, 2004–2013
Fig. IV.1.13 Annual average concentrations of PM2.5 in the ambient air in 2004–2013 at selected stations
Fig. IV.1.14 Share of localities with the exceedance of the limit value for 24-hour concentrations and annual average concentrations of PM10 and target value for the annual average concentration of PM2.5, 2000–2013
Fig. IV.1.15 Trends of PM10 and PM2.5 annual characteristics in the Czech Republic, 1996–2013
Fig. IV.1.16 Trends of selected characteristics of PM10 (index, year 1996 = 100), 1996–2013; (index, year 2000 = 100), 2000–2013 and PM2.5 (index, year 2004 = 100), 2004–2013
Fig. IV.1.17 Five-year average of annual average concentrations of PM10, 2009–2013
Fig. IV.1.18 Five-year average of annual average concentrations of PM2.5, 2009–2013
Fig. IV.1.19 Emissions of PM10 sorted out by NFR sectors, 2012
Fig. IV.1.20 Emissions of PM2.5 sorted out by NFR sectors, 2012
Fig. IV.1.21 The development of PM10 emissions, 2007–2012
Fig. IV.3.22 The development of PM2.5 emissions, 2007–2012
Fig. IV.1.23 PM10 emission density from 5x5 km squares, 2012
Fig. IV.1.24 PM2.5 emission density from 5x5 km squares, 2012
Fig. IV.2.1 Field of annual average concentration of benzo[a]pyrene in the ambient air in 2013
Fig. IV.2.2 Annual course of average monthly concentrations of benzo[a]pyrene (averages for the given type of station), 2013
Fig. IV.2.3 24-hour concentrations at the stations with the highest annual concentrations of benzo[a]pyrene in 2013
Fig. IV.2.4 Annual average concentrations of benzo[a]pyrene in the ambient air in 2002–2013 at selected stations
Fig. IV.2.5 Trends of benzo[a]pyrene annual characteristics in the Czech Republic, 1996–2013
Fig. IV.2.6 Five-year average of annual average concentrations of benzo[a]pyrene, 2009–2013
Fig. IV.2.7 Monthly average concentrations of benzo[a]pyrene in various types of localities, 2004–2013
Fig. IV.2.8 Concentrations of benzo[a]pyrene and PM10 particles in individual localities, 2008–2013
Fig. IV.2.9 Emissions of benzo[a]pyrene sorted out by NFR sectors, 2012
Fig. IV.2.10 Benzo[a]pyrene emission density from 5x5 km squares, 2012
Fig. IV.3.1 Field of annual average concentration of NO2 in 2013
Fig. IV.3.2 Annual course of average monthly concentrations of NO2 (averages for the given type of station), 2013
Fig. IV.3.3 Stations with the highest hourly concentrations of NO2 in 2013
Fig. IV.3.4 Stations with the highest exceedance of LV for annual concentrations of NO2 in 2013
Fig. IV.3.5 Field of annual average concentration of NOx in 2013
Fig. IV.3.6 24-hour concentrations at the stations with the highest annual concentrations of NOx in 2013
Fig. IV.3.7 19th highest hourly concentrations and annual average concentrations of NO2 in 2003–2013 at selected stations
Fig. IV.3.8 Trends of NO2 and NOx annual characteristics in the Czech Republic, 1996–2013
Fig. IV.3.9 Trends of selected characteristics of NO2 a NOx (index, year 1996 = 100), 1996–2013; (index, year 2000 = 100), 2000–2013
Fig. IV.3.10 Five-year average of annual average concentrations of NO2, 2009–2013
Fig. IV.3.11 Annual average concentrations of NOx and NO2 in 2003–2013 at selected rural stations
Fig. IV.3.12 Emissions of NOx sorted out by NFR sectors, 2012
Fig. IV.3.13 The development of NOx emissions, 2007–2012
Fig. IV.3.14 Nitrogen oxides emission density from 5x5 km squares, 2012
Fig. IV.4.1 Field of the 26th highest maximum daily 8-hour running average of ground-level ozone concentrations in three-year average, 2011–2013
Fig. IV.4.2 Numbers of exceedances of the target value for the maximum daily 8-hour running average of ground-level ozone concentrations in three-year average, 2011–2013
Fig. IV.4.3 Annual course of average max. 8-hour running average of O3 (averages for the given type of station), 2013
Fig. IV.4.4 Stations with the highest values of maximum daily 8-hour running average concentrations of ground-level ozone in 2011–2013
Fig. IV.4.5 Field of exposure index AOT40 values, average for 5 years, 2009–2013
Fig. IV.4.6 Stations with the highest exposure index AOT40 values in recent 5 years, 2009–2013
Fig. IV.4.7 26th highest values of maximum daily 8-hour running average of ground-level ozone concentrations (three-year average) in 2003–2013 at selected stations
Fig. IV.4.8 Trends of O3 annual characteristics in the Czech Republic, 1996–2013
Fig. IV.4.9 Trends of selected characteristics of O3 (index, year 1996 = 100), 1996–2012; (index, year 2000 = 100), 2000–2013
Fig. IV.4.10 Ozone exposure index AOT40 values in 2003–2013 at selected stations, average for 5 years
Fig. IV.4.11 Annual values of ozone exposure index AOT40 in 2009–2013 at selected stations
Fig. IV.5.1 Field of annual average concentration of benzene in the ambient air in 2013
Fig. IV.5.2 24-hour concentrations at the stations with the highest annual benzene concentrations in 2013
Fig. IV.5.3 Annual average concentrations of benzene in 2003–2013 at selected stations
Fig. IV.5.4 Trends of benzene annual characteristics in the Czech Republic, 2005–2013
Fig. IV.5.5 Five-year average of annual average concentrations of benzene, 2009–2013
Fig. IV.6.1 Field of annual average concentration of cadmium in the ambient air in2013
Fig. IV.6.2 Field of annual average concentration of arsenic in the ambient air in 2013
Fig. IV.6.3 Short-term average concentrations of lead in the ambient air in 2013 at selected stations
Fig. IV.6.4 Short-term average concentrations of cadmium in the ambient air in 2013 at selected stations
Fig. IV.6.5 Short-term average concentrations of arsenic in the ambient air in 2013 at selected stations
Fig. IV.6.6 Short-term average concentrations of nickel in the ambient air in 2013 at selected stations
Fig. IV.6.7 Annual average concentrations of lead in the ambient air in 2003–2013 at selected stations
Fig. IV.6.8 Annual average concentrations of cadmium in the ambient air in 2003–2013 at selected stations
Fig. IV.6.9 Annual average concentrations of arsenic in the ambient air in 2003–2013 at selected stations
Fig. IV.6.10 Annual average concentrations of nickel in the ambient air in 2003–2013 at selected stations
Fig. IV.6.11 Five-year average of annual average concentrations of cadmium, 2009–2013
Fig. IV.6.12 Five-year average of annual average concentrations of arsenic, 2009–2013
Fig. IV.6.13 Trends of heavy metals annual characteristics in the Czech Republic, 2005–2013
Fig. IV.6.14 Emissions of Pb sorted out by NFR sectors, 2012
Fig. IV.6.15 Emissions of Cd sorted out by NFR sectors, 2012
Fig. IV.6.16 Emissions of As sorted out by NFR sectors, 2012
Fig. IV.6.17 Emissions of Ni sorted out by NFR sectors, 2012
Fig. IV.6.18 Pb emission density from 5x5 km squares, 2012
Fig. IV.6.19 Cd emission density from 5x5 km squares, 2012
Fig. IV.6.20 As emission density from 5x5 km squares, 2012
Fig. IV.6.21 Ni emission density from 5x5 km squares, 2012
Fig. IV.7.1 Field of the 4th highest 24-hour concentration of SO2 in 2013
Fig. IV.7.2 Stations with the highest hourly concentrations of SO2 in 2013
Fig. IV.7.3 Stations with the highest 24-hour concentrations of SO2 in 2013
Fig. IV.7.4 Field of annual average concentration of SO2 in 2013
Fig. IV.7.5 Field of average concentration of SO2 in the winter period 2013/2014
Fig. IV.7.6 24-hour concentrations at the stations with the highest annual concentrations of SO2 in 2013
Fig. IV.7.7 24-hour concentrations at the stations with the highest winter concentrations of SO2 in the winter period 2013/2014
Fig. IV.7.8 4th highest 24-hour concentrations and 25th highest hourly concentrations of SO2 in 2003–2013 at selected stations
Fig. IV.7.9 Trends of SO2 annual characteristics in the Czech Republic, 1996–2013
Fig. IV.7.10 Trends of selected characteristics of SO2 (index, year 1996 = 100), 1996–2013; (index, year 2000 = 100), 2000–2013
Fig. IV.7.11 Annual average concentrations of SO2 in 2003–2013 at selected rural stations
Fig. IV.7.12 Winter average concentrations of SO2 in 2003/2004–2013/2014 at selected rural stations
Fig. IV.7.13 Emissions of SO2 sorted out by NFR sectors, 2012
Fig. IV.7.14 The development of SO2 emissions, 2007–2012
Fig. IV.7.15 Sulphur dioxide emission density from 5x5 km squares, 2012
Fig. IV.8.1 Stations with the highest values of maximum daily 8-hour running average concentrations of CO in 2013
Fig. IV.8.2 Maximum daily 8-hour running average concentrations of CO in 2003–2013 at selected stations
Fig. IV.8.3 Emissions of CO sorted out by NFR sectors, 2012
Fig. IV.8.4 The development of CO emissions, 2007–2012
Fig. IV.8.5 Carbon monoxide emission density from 5x5 km squares, 2012
Fig. IV.9.1.1 Annual average concentrations of fethane and isoprene in the ambient air at selected stations, 1997–2013
Fig. IV.9.1.2 Emissions of VOC sorted out by NFR sectors, 2012
Fig. IV.9.1.3 The development of VOC emissions, 2007–2012
Fig. IV.9.2.1 Average monthly concentrations of elemental carbon and organic carbon in the Observatory Košetice, 2009–2013
Fig. IV.9.2.2 Average monthly shares of elemental carbon in total carbon in the Observatory Košetice, 2009–2013
Fig. IV.9.2.3 Average monthly shares of elemental carbon in PM2.5 concentrations in the Observatory Košetice, 2009–2013
Fig. IV.9.3.1 Emissions of NH3 sorted out by NFR sectors, 2012
Fig. IV.9.3.2 The development of NH3 emissions, 2007–2012
Fig. V.1 Trends of SO2, NO2 and CO (1996–2013) and benzene (2005–2013) annual characteristics in agglomerations
Fig. V.2 Trends of PM10 (1996–2013), PM2.5 (2004–2013) and benzo[a]pyrene (2005–2013) annual characteristics in agglomerations
Fig. V.1.1 Number of exceedances of 24-hour PM10 limit value in selected localities and the 36th highest 24-hour concentration PM10 at individual types of stations, agglomeration of Prague, 2006–2013
Fig. V.1.2 Average annual PM10 concentrations in selected localities and at individual types of stations, agglomeration of Prague, 2006–2013
Fig. V.1.3 Number of days with concentrations of PM10 > 50 µg.m-3 in individual months, incl. total number of exceedances, agglomeration of Prague, 2013
Fig. V.1.4 Average annual PM2.5 concentrations, agglomeration of Prague, 2004–2013
Fig. V.1.5 Numbers of exceedances of the hourly limit value for NO2 at the traffic station Prague 2-Legerova (hot spot), agglomeration of Prague, 2003–2013
Fig. V.1.6 Average annual NO2 concentrations in selected localities and at individual types of stations, agglomeration of Prague, 2006–2013
Fig. V.1.7 Average annual benzo[a]pyrene concentrations, agglomeration of Prague, 2000–2013
Fig. V.1.8 Numbers of exceedances of the limit value of O3 in the average for three years, agglomeration of Prague, 2006–2013
Fig. V.1.9 Field of the annual concentration of NO2, agglomeration of Prague, 2013
Fig. V.1.10 Field of the 36th highest 24-hour concentration of PM10, agglomeration of Prague, 2013
Fig. V.1.11 Emissions of selected pollutants listed according to REZZO in the agglomeration of Prague
Fig. V.2.1 Average annual PM10 concentrations in selected localities and at individual types of stations, agglomeration of Brno, 2006–2013
Fig. V.2.2 Average monthly PM10 concentrations in the locality Kuchařovice (average for 2005–2012)
Fig. V.2.3 Average annual PM2.5 concentrations, agglomeration of Brno, 2004–2013
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, 2006–2013
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, 2013
Fig. V.2.6 Trend of hourly PM10 and NO concentrations in the locality Brno-střed, division into weekdays and weekends, averages for the years 2005–2013
Fig. V.2.7 Average annual NO2 concentrations in selected localities and at individual types of stations, agglomeration of Brno, 2006–2013
Fig. V.2.8 Average annual benzo[a]pyrene concentrations, agglomeration of Brno, 2006–2013
Fig. V.2.9 Field of the annual concentration of NO2, agglomeration of Brno, 2013
Fig. V.2.10 Field of the 36th highest 24-hour concentration of PM10, agglomeration of Brno, 2013
Fig. V.3.1 Average annual PM10 concentrations in selected localities and at individual types of stations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2006–2013
Fig. V.3.2 Average annual PM2.5 concentrations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2004–2013
Fig. V.3.3 Number of days with concentrations of PM10 > 50 µg.m-3, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2013
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, 2006–2013
Fig. V.3.5 Average annual NO2 concentrations in selected localities and at individual types of stations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2006–2013
Fig. V.3.6 Average annual benzo[a]pyrene concentrations, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2000–2013
Fig. V.3.7 Number of exceedances of the target value of O3 in the average for three years, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2006–2013
Fig. V.3.8 Most significant stationary sources of TSP, NOx and SO2 emissions, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2012
Fig. V.3.9 Field of the annual concentration of NO2, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2013
Fig. V.3.10 Field of the 36th highest 24-hour concentration of PM10, agglomeration of Ostrava/Karviná/Frýdek-Místek, 2013
Fig. VI.1 SVRS areas and representative stations for PM10
Fig. VI.2 SVRS areas and representative stations for O3
Fig. VI.3 Smog situations and regulations for PM10 in 2013 in the SVRS areas in which at least one smog situation was announced
Fig. VII.1 Areas with exceeding of the health protection limit values, ground-level ozone excluded, 2013
Fig. VII.2 Areas with exceeding of the health protection limit values, incl. ground-level ozone, 2013
Fig. VII.3 Limit value (LV) exceedances in the Czech Republic, % of the area, 2006–2013
Fig. VII.4 Areas with exceeding of the health protection limit values, ground-level ozone excluded, 2013
Fig. VII.5 Areas with exceeding of the health protection limit values, incl. ground-level ozone, 2013
Fig. VIII.1 Average concentrations of PM10 and PM2.5 in the European cities with 250,000–350, 000 inhabitants
Fig. VIII.2 Concentrations of PM2.5, benzo[a]pyrene, NO2 (annual average) and O3 (max. daily 8-hour average) in Europe, 2011 (Source: EEA 2013a)
Fig. VIII.3 36th highest value of maximum daily average of PM10 concentration, 2011 (Source: ETC/ACM 2013)
Fig. VIII.4 Annual mean concentrations of benzo[a]pyrene in Europe, 2011(Source: EEA 2013a)
Fig. VIII.5 Annual mean concentrations of NO2 in Europe, 2011(Source: EEA 2013a)
Fig. VIII.6 26th highest value of maximum daily 8-hour running average of ground-level ozone concentrations, 2011(Source: ETC/ACM 2013)
Fig. IX.1 Station networks monitoring atmospheric precipitation quality and atmospheric deposition, 2013
Fig. IX.2 Fields of annual wet deposition of sulphur (SO42- - S), 2013
Fig. IX.3 Fields of annual dry deposition of sulphur (SO2 - S), 2013
Fig. IX.4 Fields of annual total deposition of sulphur, 2013
Fig. IX.5 Fields of annual throughfall deposition of sulphur, 2013
Fig. IX.6 Fields of annual wet deposition of nitrogen (NO3- - N), 2013
Fig. IX.7 Fields of annual wet deposition of nitrogen (NH4+ - N), 2013
Fig. IX.8 Fields of annual total wet deposition of nitrogen, 2013
Fig. IX.9 Fields of annual dry deposition of nitrogen (NOx - N), 2013
Fig. IX.10 Fields of annual total deposition of nitrogen, 2013
Fig. IX.11 Fields of annual wet deposition of hydrogen ions, 2013
Fig. IX.12 Fields of annual dry deposition of hydrogen ions corresponding to SO2 and NOx deposition, 2013
Fig. IX.13 Fields of annual total deposition of hydrogen ions, 2013
Fig. IX.14 Fields of annual wet deposition of chloride ions,, 2013
Fig. IX.15 Fields of annual wet deposition of lead ions, 2013
Fig. IX.16 Fields of annual dry deposition of lead, 2013
Fig. IX.17 Fields of annual wet deposition of cadmium ions, 2013
Fig. IX.18 Fields of annual dry deposition of cadmium, 2013
Fig. IX.19 Fields of annual wet deposition of nickel ions, 2013
Fig. IX.20 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, 1995–2013
Fig. IX.21 The development of the ratio of nitrate/sulphate concentrations in atmospheric deposition (expressed as µeq. l-1) at the CHMI stations, 1998–2013
Fig. IX.22 The development of annual wet deposition at selected stations in 1991–2013, Czech Republic
Fig. X.1 Emissions of carbon dioxide structured by sectors, 1990–2012
Fig. X.2 Emissions of methane structured by sectors, 1990–2012
Fig. X.3 Emissions of nitrous oxide structured by sectors, 1990–2012
Fig. X.4 Emissions of F-gases, 1995–2012
Fig. X.5 Carbon dioxide emissions from the plants registered in EU ETS, 2005–2013
Fig. XI.1 Scheme of ISKO’s links to data sources and co-operating systems 2013
Fig. XI.2 Monitoring of basic pollutants in selected organisations – development
Fig. XII.1 Diagram showing the variogram parameters and the fitted spherical functions in 2013