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6.2.1. Behaviour, effects, emissions
Nitrogen oxides (NOx) has natural and anthropogenic sources. The natural sources (bacterial and volcanic action, and lightening) cause a low-level background NO2 concentration. The main anthropogenic source is combustion of fossil fuel, which causes elevated concentrations in near-source areas. NOx is usually considered the sum of nitrogen monoxide (NO) and nitrogen dioxide (NO2). In the anthropogenic emissions, NO dominates (typically 80-90%). In the atmosphere, NO reacts quickly with O3 to form NO2. Further reactions depend mainly upon the concentrations of VOC in the air, and the intensity of sunlight. There is a photochemical equilibrium condition between NO, NO2 and O3 with the equilibrium concentrations dependent upon the concentration of OH and other radicals resulting from photochemical reactions. NO2 is eventually converted to HNO3 by reaction with OH radicals. HNO3 is then removed from the atmosphere by wet deposition, and to a lesser extent by dry depositions, adding to the acid deposition problem.
Major sources in most urban areas today are motor vehicle exhaust, which dominates, and combustion of fossil fuels in stationary installations. Large power plants with tall stacks are significant sources of NOx which, however, seldom causes high exposures in nearby areas.
Urban annual average NO2 concentrations are generally in the range 20-90 µg/m3, and peak daily and hourly concentrations may reach several hundred and more than 500 µg/m3 respectively in periods of poor dispersion.
NO2 affects the respiratory system, and a range of effects have been reported from short-term or long-term exposures from controlled human exposure experiments and epidemiological studies: altered lung functions and symptomatic effects, increased prevalence of acute respiratory illness and symptoms, lung tissue damage (at high exposures), increased susceptibility to infections. Young children and individuals with respiratory system decease, such as asthmatics and other chronic respiratory illnesses are those most sensitive to NO2 exposures.
NOx and NO2 contribute to the acid deposition problem, and cause visible injury to vegetation at concentration higher than those occurring in ambient air in Europe, but may occur near a few point sources.
The trend in NOx emissions in Europe (see Figure 6.19) has been calculated and reported by EMEP (Berge et al., 1995). NOx emissions in the EMEP area changed little prior to 1985. Later, emission data show a very rapid increase, culminating in 1989, and after that it has declined down to the pre-1985 emission level. It should be noted that the accuracy of emission numbers before 1985, or even before 1990, may be limited, especially for Eastern Europe. After 1990, the decline is mostly due to reported reduced emissions in East European countries, but also decreasing emissions in West European countries, partly due to the introduction of catalyst cars.
6.2.2. Air Quality Limit and Guide Values
EU Limit and Guide values and WHO Guideline values for NO2 are given in Table 6.5. The WHO Guideline values are maximum values and are not to be exceeded.
Table 6.5: EU Limit and Guide Values for NO2 (µg/m3) EU Council Directive 85/203/EEC WHO Guideline values for NO2 (µg/m3).
Limit values | Median of 1 h values |
98 percentile of <1 h values |
Year | 200 | |
Guide values | ||
Year | 50 | 135 |
WHO Guideline values | Maximum 1 h average |
Maximum 24 h average |
400 | 150 |
6.2.3. Urban and local NO2 concentrations
In Appendix B NO2 data from 17 countries are given. The stations are ranged according to the 98 percentile of hourly values. The stations with the highest values are given in Table 6.6. Also the maximum
and median hourly values are given.
Figure 6.20 show maximum, 98 percentile and median hourly values for selected stations and cities. The figure does not show much lower concentrations in the Nordic countries as the SO2 data do. 98 percentile and median values do not vary much over Europe, except for higher values in Spain and Greece. As shown in Table 6.6 and Appendix B, stations in Italy and Portugal also have high 98 percentile values.
NO2 data from the selected cities in Figure 5.1/Table 5.2 are shown in Figure 6.21 and Figure 6.22. These figures give the median and 98 percentile of hourly values, respectively. These figures, together with Table 6.6 and Appendix B, show the highest NO2 values in southern Europe, and some large cities like London and Paris.
Table 6.6: 1 h maximum, 98 percentile and median NO2 values for 1993 for European cities ranged according to the 98
percentile hourly values (µg/m3).
Country |
City |
Maximum |
98- percentile |
Median |
||
Name | Class | Station | ||||
Italy | Bologna | Via Marconi | 348 | |||
Portugal | Lisboa | Entrecampos | 311 | 69 | ||
Italy | Milano | Statuto | 289 | |||
Italy | Piacenza | Via Giordani | 264 | |||
Italy | Milano prov. | Monza | 256 | |||
Italy | Milano prov. | Sesto s. g. comune | 252 | |||
Greece | Athens | 1 | Patission 147 | 554 | 247 | 98 |
Italy | Milano | Senato | 247 | |||
Italy | Milano | Juvara | 246 | |||
Italy | Milano | Zavattari | 233 | |||
Italy | Milano prov. | Lainate | 226 | |||
Italy | Milano | Marche | 222 | |||
Italy | Milano | Liguria | 218 | |||
Italy | Bologna | Via Matteotti | 214 | |||
Italy | Bologna | Via Irnerio I | 211 | |||
Italy | Milano prov. | Legnano Tosi | 202 | |||
Italy | Roma | Fermi | 198 | |||
Italy | Torino | Via madama Cristina | 198 | |||
Italy | Torino | Via Consolata | 197 | |||
Italy | Genova | C. SO Europa | 195 | |||
Italy | Roma | Gondar | 195 | |||
Italy | Genova | Acquasola | 193 | |||
Italy | Milano prov. | Villasanta | 192 | |||
Italy | Milano prov. | Agrate | 192 | |||
Italy | Milano prov. | Limito | 192 | |||
Italy | Bologna | Via Emilia Ponente | 190 | |||
Italy | Roma | M. Grecia | 190 | |||
Italy | Venezia (ind. zone) | Stab. Montedipe 1 | 190 | |||
Italy | Milano prov. | Settimo | 188 | |||
Italy | Torino | Corso Vercelli | 188 | |||
Italy | Torino | Via Guido Reni | 188 | |||
Spain | Madrid | 1 | Plaza España | 470 | 187 | 57 |
Italy | Venezia (ind. zone) | Piazza s. Antonio (Marghera) | 186 | |||
Italy | Milano prov. | Inzago | 186 | |||
Italy | Milano prov. | Corsico | 184 | |||
Italy | Milano prov. | Melegnano | 183 | |||
Portugal | Carregado | Cast. Ribatejo | 181 | |||
Italy | Milano prov. | Cuggiono | 181 | |||
Italy | Roma | Preneste | 179 | |||
Italy | Genova | Villa Serra | 178 | |||
Italy | Piacenza | Via Taverna | 178 | |||
Spain | Madrid | 1 | Cuatro Caminos | 448 | 177 | 72 |
Italy | Milano prov. | Rivolta | 176 | |||
Italy | Milano prov. | Robecchetto | 176 | |||
Italy | Firenze | Mosse | 174 | |||
Italy | Piacenza | Via Alberoni | 174 | |||
Italy | Milano prov. | Legnano com. | 173 | |||
France | Paris | 1 | R.N 13 Rue Malmaison | 424 | 172 | 69 |
Italy | Bologna | Fiera | 171 | |||
Italy | Bologna | P. Za dei Martiri | 170 |
Figure 6.20: 1 h maximum, 98 percentile and median NO2 values for 1993 for selected stations and cities (µg/m3).
Figure 6.21: NO2 median 1h values in selected cities (µg/m3).
Figure 6.22: NO2 98 percentile 1h values in selected cities (µg/m3).
Exceedances
Table 6.7 shows stations with exceedances of the EU Limit value for
NO2
(98 percentile of hourly values, 200 µg/m3). This limit value is
rather high. It is exceeded at one station in Greece and Portugal and at a number of
stations in Italy. Some stations in Austria have rather high maximum 1/2h NO2
values, but 98 percentile values are not given. Probably the EU Limit value is not
exceeded in Austria. From Eastern Europe there are no available NO2
data to be compared with the EU Limit value.
Table 6.8 shows exceedances of EU Guide values and WHO Guideline values for NO2. WHO Guideline values are much higher than EU Guide values and are exceeded only in a few countries. EU Guide values seems to be exceeded commonly in Western Europe. Data from Eastern Europe are not available.
Table 6.7: Exceedances of EU Limit Values for NO2.
Country |
City |
Station name |
1h values 1 year |
P98 >200 |
|||
Greece | Athens | Patission 147 |
|
Italy | Genova | Via Cantore |
|
Piazza Masnata |
|
||
Bologna | Via Marconi |
|
|
Via Matteotti |
|
||
Via Irnerio I |
|
||
Firenze | Roselli |
|
|
Milano | Marche |
|
|
Invara |
|
||
Zavattari |
|
||
Liguria |
|
||
Verziere |
|
||
Senato |
|
||
Cenisio |
|
||
Aquileia |
|
||
Statuto |
|
||
Milano (province) | Sesto s. g. Comune |
|
|
Monza |
|
||
Cinisello |
|
||
Pero |
|
||
Arrese |
|
||
Lainate |
|
||
Legnano Tosi |
|
||
Piacenza | Via Giordani |
|
|
Portugal | Lisboa | Entrecampos |
|
** Data availability <75%.
Table 6.8: Exceedances of EU and WHO Guide(line) values for NO2.
Country |
City |
Station |
EU Guide Values | WHO Guideline Values | ||
Median 1h > 50 | P98 1h >135 | Max. 1h >400 | Max. 24 h >150 | |||
Austria | Graz | Süd | 151 | |||
(mean values) | Linz | 24-er-Turm | 172 | |||
BH-Urfahr | 155 | |||||
Kleinmünchen | 162 | |||||
ORF-Zentrum | 167 | |||||
Salzburg | Rudolfplatz | 71 | ||||
Wien | Hietzinger Kai | 74 | ||||
France | Lyon | Lyon Berthelot | 80 | 160 | 452 | 166 |
Lyon Garibaldi | 65 | 162 | 481 | |||
Lyon Puits Gaillot | 67 | 164 | 403 | |||
Paris | Neuilly/Seine (92) | 58 | 418 | 177 | ||
Paris Ch. de Mars | 52 | 435 | 166 | |||
Paris Tour St-Jacques | 63 | 150 | 167 | |||
R.N 13 Rue Malmaison | 69 | 172 | 424 | 197 | ||
Rue Danzig (15ème) | 61 | 145 | 437 | 159 | ||
Tour Eiffel (1er et.) | 50 | 154 | 172 | |||
Strasbourg | rue du 22 novembre | 50 | ||||
Germany | Berlin | Charlottenburg | 56 | 155 | ||
Düsseldorf | Düsseldorf-Mörsenbroich | 61 | ||||
Erfurt | Erfurt, Krämpf. | 137 | ||||
Essen | Essen-Ost | 53 | ||||
Gera | Gera, Frieder. | 141 | ||||
Hamburg | Stresemannstrasse | 58 | 142 | |||
Hannover | Göttinger strasse | 136 | ||||
Karlsruhe | Karlsruhe-Mitte | 51 | ||||
Koblenz | Friedrich-Ebert-Ring | 57 | ||||
Ludwigshafen-Frankental | Frankental | 57 | ||||
Mundenheim | 51 | |||||
Mainz-Mombach | Parcusstrasse | 67 | 163 | |||
Wiesbaden | W-Ringkirche | 136 | ||||
Greece | Athens | Patission 147 | 98 | 247 | 253 | |
Pireas Platia Dimotikou | 67 | 136 | ||||
Italy | Bologna | Fiera | 171 | |||
P. Za dei Martiri | 170 | |||||
Via Emilia Ponente | 190 | |||||
Via Irnerio I | 211 | |||||
Via Marconi | 348 | |||||
Via Matteotti | 214 | |||||
Firenze | Mosse | 174 | ||||
Via Bassi | 145 | |||||
Genova | Acquasola | 193 | ||||
C. SO Europa | 195 | |||||
Villa Serra | 178 |
Country |
City |
Station |
EU Guide Values | WHO Guideline Values | ||
Median 1h > 50 | P98 1h >135 | Max. 1h >400 | Max. 24 h >150 | |||
Italy (contd.) | Milano | Juvara | 246 | |||
Liguria | 218 | |||||
Marche | 222 | |||||
Senato | 247 | |||||
Statuto | 289 | |||||
Zavattari | 233 | |||||
Milano prov. | Agrate | 192 | ||||
Cassano dAdda | 169 | |||||
Corsico | 184 | |||||
Cuggiono | 181 | |||||
Galliate | 166 | |||||
Inzago | 186 | |||||
Lainate | 226 | |||||
Legnano com. | 173 | |||||
Legnano Tosi | 202 | |||||
Limito | 192 | |||||
Lodi | 159 | |||||
Melegnano | 183 | |||||
Monza | 256 | |||||
Rivolta | 176 | |||||
Robecchetto | 176 | |||||
Sesto s. g. comune | 252 | |||||
Settimo | 188 | |||||
Turbigo | 143 | |||||
Villasanta | 192 | |||||
Modena | Cavour | 141 | ||||
Via Giardini | 167 | |||||
Piacenza | Via Alberoni | 174 | ||||
Via Giordani | 264 | |||||
Via Taverna | 178 | |||||
Ravenna | S.A.P.I.R | 136 | ||||
Roma | Fermi | 198 | ||||
Francia | 159 | |||||
Gondar | 195 | |||||
M. Grecia | 190 | |||||
Preneste | 179 | |||||
Torino | Corso Vercelli | 188 | ||||
Parco Lingotto | 160 | |||||
Via Consolata | 197 | |||||
Via Guido Reni | 188 | |||||
Via madama Cristina | 198 | |||||
Trento | Trento | 163 | ||||
Trento Nord | 144 | |||||
Venezia | Piazza s. Antonio (Marghera) | 186 | ||||
(ind. zone) | Stab. Montedipe 1 | 190 | ||||
The Netherlands | Utrecht | Witte Vrouwenstraat | 58 |
Country |
City |
Station |
EU Guide Values | WHO Guideline Values | ||
Median 1h > 50 | P98 1h >135 | Max. 1h >400 | Max. 24 h >150 | |||
Norway | Bergen | CMI | 59 | 135 | 204 | |
(based upon 24h | Drammen | Engene | 74 | |||
values) | Fredrikstad | Broch street | 50 | |||
Oslo | St. Olavs square | 50 | ||||
Skien | Kings street | 57 | ||||
Stavanger | Handelens hus | 63 | ||||
Trondheim | Torget | 57 | ||||
Portugal | Carregado | Cast. Ribatejo | 181 | |||
Faro | Faro | 80 | 141 | |||
Lisboa | Benéfica | 69 | 151 | |||
Entrecampos | 69 | 311 | ||||
Rua da Prata | 52 | 137 | ||||
Setúbal | Setubal-Cicade | 167 | ||||
Spain | Barcelona | Molina Pl. | 55 | |||
Madrid | Arturo Soria | 53 | 159 | |||
Carlos V | 57 | 151 | 154 | |||
Cuatro Caminos | 72 | 177 | 448 | 184 | ||
Plaza Castilla | 58 | 141 | ||||
Plaza España | 57 | 187 | 470 | 189 | ||
Villaverde | 72 | 151 | ||||
Switzerland | Basel | Feldbergstrasse | 57 | |||
(mean values) | Bern | Bern | 57 | |||
Genève | Ile | 60 | ||||
Lausanne | Lausanne | 50 | ||||
Rue César Roux 2 | 56 | |||||
Zürich | Schimmelstrasse | 57 | ||||
United Kingdom | Edinburgh | Edinburgh centre | 50 | |||
Leeds | Leeds centre | 50 | ||||
Liverpool | Liverpool centre | 50 | ||||
London | Bridge Place | 63 | 136 | 192 | ||
London Bloomsbury | 65 | |||||
Newcastle | Newcastle centre | 54 |
Trends
Figure 6.23-Figure 6.28 show, as examples, trends in NO2 data on an annual basis for some selected stations in different countries. The figures show the maximum, 98 percentile and median of 1 h data from Denmark, United Kingdom, the Netherlands, Belgium, Germany (only 98 percentile), Switzerland (mean instead of median), Spain and Greece, while Norwegian values are based on 24 h data.
Most stations show a relative stable NO2 level for the last 10 years, even though some stations might show slightly decreasing median and mean values over the last few years, for instance Aalborg, Rotterdam, Bruxelles and several Swiss towns. Rather high values, especially maximum values, are measured in Athens.
Figure 6.23: NO2 trend in Norway 1986-1994 (only winter data and 24 h values) (µg/m3). Data from national reports.
Figure 6.24: NO2 trend in Aalborg, Denmark 1982-1994 and Bridge Place (Greater London), UK 1990-93 (µg/m3). APIS data.
Figure 6.25: NO2 trend in Rotterdam, the Netherlands 1981-1994 and Bruxelles, Belgium 1980-1994 (µg/m3). APIS data.
Figure 6.26: NO2 trend in Bremen, Germany 1987-1993 (µg/m3). Data from Bremen State report.
Figure 6.27: NO2 trend in Switzerland 1984-1993 (µg/m3). The Swiss trend figures are based on œ h values, and the numbers given are the 95 percentile and mean values. Data from national report.
Figure 6.28: NO2 trend in Greece 1983-1993 (µg/m3). APIS data.
6.2.4. Regional nitrogen compound concentrations and deposition
The following presentation is based directly upon the 1993 EMEP data report (EMEP, 1995).
Concentrations
Nitrogen dioxide
The number of sites reporting NO2 data during 1993 were 30% less than the number of sites reporting SO2. For this reason and due to the fact that there are larger local NO2 concentrations, and larger inaccuracies in the measurements of NO2, the uncertainties in the NO2 concentrations in Figure 6.29 are generally much larger than for SO2. The reservations made for SO2 with respect to site location and presence of higher concentrations in industrialised, densely populated areas are also valid for NO2. In addition, even higher concentrations will be found in areas with heavy traffic.
In northern Scandinavia, the annual values are below 1 µg N/m3. For United Kingdom, no NO2 data are available for 1993. A decreasing gradient from England over the Netherlands to Germany is indicated by the Irish and the Continental results. The highest concentrations of NO2, >6 µg N/m3, are reported from four stations in Spain, one in Italy and one in the Netherlands. In central Europe the NO2 concentrations range from 2 to 6 µg N/m3.
Deposition
Nitrate in precipitation
Annual averages of nitrate in precipitation is presented in Figure 6.30. The pattern is somewhat similar to that of sulphate in precipitation. Most areas have annual concentrations lower than 0.6 mg N/l. In Portugal. western Ireland and northern Scandinavia, the annual averages are lower than 0.2 mg N/l. The areas with the highest levels are mainly located in eastern parts of Europe; Poland and towards south-east. High nitrate concentrations are also measured at stations in Germany, Italy and Spain. There is a sharp gradient over the Iberian peninsula, with low concentrations in the west and high concentrations in north-eastern Spain.
Ammonium in precipitation
The ammonium levels presented in Figure 6.31, are also relatively low. In contrast to the anthropogenic sources of NOx giving nitrate in precipitation after a series of photochemical reaction, the sources for ammonia, which give ammonium are mainly related to agricultural activities, including domestic animal keeping and the conversion from gaseous ammonia to ammonium is relatively rapid. The pattern for ammonium is usually quite different from that of nitrate and sulphate. Two maximum areas are indicated, one in south-western France and one in southern Poland, Ukraine and Romania. Concentrations of ammonium in precipitation higher than 1 mg N/l are measured at stations in Lithuania and Poland. Concentrations around 1 mg N/l are measured at stations in France and Croatia. In most parts of Europe the concentrations are lower than 0.7 mg N/l and in the outskirts of Europe, in northern Scandinavia, even below 0.2 mg N/l.
Figure 6.29: Nitrogen dioxide in rural areas 1993, annual average
(µg N/m3).
Factor: 3.28.
Figure 6.30: Nitrate in precipitation 1993 (mg N/l).
Factor: 4.43.
Figure 6.31: Ammonium in precipitation 1993 (mg N/l).
Factor: 1.21.
For references, please go to https://www.eea.europa.eu/publications/2-9167-057-X/page019.html or scan the QR code.
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