KAZALCI OKOLJA

Nitrogen oxides (NOx) play an important role in air pollution phenomena such as acidification, eutrophication and photochemical smog. The main source of NOx within urban areas is use of fuel in traffic, combustion plants and power plants. Otherwise, nitrogen dioxide (NO2) concentrations are also determined by meteorological conditions. The amount of NOx is crucially influenced by ozone.

The indicator shows the frequency of exceeding the 1-hour limit concentration values of NO2 exceeding 200 μg/m3 and average annual NO2 concentrations (limit annual value is 40 μg/m3).


Charts

Figure ZR06-1: Number of hours with exceeded average 1-hour limit value of NO2 concentration (dovoljeno preseganje znaša 18 ur)
Sources:

National authomatic measurement air quality network database, Environmental Agency of the Republic of Slovenia, 2008

Show data
1992 1993 1994 1995 1996 1997 1998 1999 2000 2001
Ljubljana Figovec number of hours 15 21 0 0 0 0 3 2 0 0
Ljubljana Bežigrad number of hours np np np np np np np np np np
Maribor number of hours 0 3 2 0 0 0 0 0 7 0
Celje number of hours 5 9 14 6 1 np 0 0 0 0
Trbovlje number of hours np np np np np 0 0 0 0 0
Murska Sobota - Rakičan number of hours np np np np np np np np np np
Nova Gorica number of hours np np np np np np np np np np
2002 2003 2004 2005 2006 2007 2007
Ljubljana Figovec number of hours 0 np np np np np np
Ljubljana Bežigrad number of hours np 0 0 0 0 0 0
Maribor number of hours 0 0 0 0 1 2 0
Celje number of hours 0 0 0 0 0 0 0
Trbovlje number of hours 0 0 0 0 0 0 0
Murska Sobota - Rakičan number of hours 0 0 0 0 0 0 0
Nova Gorica number of hours 0 0 0 0 0 0 0
Figure ZR06-2: Average annual concentration of NO2 (annual limit value is 40 μg/m3)
Sources:

National authomatic measurement air quality network database, Environmental Agency of the Republic of Slovenia, 2008

Show data
1992 1993 1994 1995 1996 1997 1998 1999 2000 2001
Ljubljana Figovec µg/m3 53 50 44 38 39 36 42 49 38 36
Ljubljana Bežigrad µg/m3 np np np np np np np np np np
Maribor µg/m3 54 57 48 39 39 38 39 39 44 38
Celje µg/m3 34 41 40 35 33 np 23 28 30 26
Trbovlje µg/m3 np np np np np 29 29 26 28 np
Murska Sobota - Rakican µg/m3 np np np np np np np np np np
Nova Gorica µg/m3 np np np np np np np np np np
2002 2003 2004 2005 2006 2007 2008
Ljubljana Figovec µg/m3 np np np np np np np
Ljubljana Bežigrad µg/m3 31 32 29 27 29 28 29
Maribor µg/m3 36 37 31 33 39 37 34
Celje µg/m3 24 27 24 26 28 23 21
Trbovlje µg/m3 28 32 26 24 23 22 23
Murska Sobota - Rakican µg/m3 14 14 11 14 15 17 16
Nova Gorica µg/m3 27 27 25 24 24 25 30

Goals

The main aim of air quality management is reduction of air pollution in Slovenia caused by NO2, as stated in the Decree on Sulphur Dioxide, Nitrogen oxides, Particulate Matter and Lead in Ambient Air (OJ RS, No 52/02) and the EU Directive (1999/30/EC). Legislation provides that average 1-hour concentration of NO2 may not exceed the limit value of 200 μg/m3 more than 18 times per calendar year. Annual NO2 concentration, however, may not exceed 40 μg/m3. Air emission management and pollution reduction is also a target of the National Environmental Action Programme.


NO2 concentrations have specific daily and weekly cycle, caused by traffic jams and annual cycle, caused by weather conditions, which are more favourable in the summer. The highest NO2 concentrations are found at roadside locations. The use of catalytic converters in vehicles led to a reduction in emissions, but due to increased traffic not significant. Figure 17-1 clearly shows that in urban areas Slovenia has already achieved the required standards relating to exceedances of 1-hour limit values at individual monitoring sites, since 2001 there was none recorded. Average annual values of NO2 (Figure 17-2), as well, have been maintained below the limit value and individual monitoring sites show a slight downward trend. Reduction of NO2 concentrations affects favourably to human health, since long-term exposure to high concentration can lead to respiratory organ infections.

Analyses of NO2 concentration measurements in other European countries indicate a slightly downward trend in annual value since 1996.


Methodology

The data for Slovenia are taken from the National authomatic measurement air quality network database maintained at the Monitoring Office (Environmental Agency of the Republic of Slovenia). The database is updated monthly; the data are available in their entirety upon the completion of final annual review.

Information on the ANAS automatic network monitoring sites: Ljubljana had two monitoring sites – Figovec and Bežigrad. By the end of 2001, Figovec monitoring site was put out of operation, Ljubljana Bežigrad monitoring site is not under dirrect traffic unfluence, but still are the concentrations measured here among the highest. The monitoring site in Maribor and Trbopvlje are located directly at the carriageway in the city centre, near an intersection; therefore the air samples show a higher level of traffic-related pollution. In Celje, measurements are taken in the hospital complex located just outside the city centre, with lower concentrations measured. Monitoring site in Nova Gorica is placed on the edge of the city. The Rakičan by Murska Sobota monitoring site is representative foer rural area in the vicinity of a town.


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