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Report - DCE - Nationalt Center for Miljø og Energi

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The considerable variations from one year to another in military jet fuel consumption<br />

are due to planning and budgetary reasons, and the passing demand<br />

<strong>for</strong> flying activities. Consequently, <strong>for</strong> some years, a certain amount of<br />

jet fuel stock-building might disturb the real picture of aircraft fuel consumption.<br />

Civil aviation has decreased until 2004, since the opening of the<br />

Great Belt Bridge in 1997, both in terms of number of flights and total jet fuel<br />

consumption. After 2004 an increase in the consumption of jet fuel is noted<br />

until 2007/2008.<br />

#VOLFST<br />

The residual oil and diesel oil fuel consumption fluctuations reflect the<br />

quantity of fuel sold in Denmark to international ferries, international warships,<br />

other ships with <strong>for</strong>eign destinations, transport to Greenland and the<br />

Faroe Islands, tank vessels and <strong>for</strong>eign fishing boats. For jet petrol, the sudden<br />

fuel consumption drop in 2002 is explained by the recession in the air<br />

traffic sector due to the events of September 11, 2001 and structural changes<br />

in the aviation business. In 2009, the impact of the global financial crisis on<br />

flying activities becomes very visible.<br />

3-<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

1985<br />

1987<br />

1989<br />

1991<br />

1993<br />

1995<br />

1997<br />

1999<br />

2001<br />

2003<br />

2005<br />

2007<br />

2009<br />

Jet fuel Diesel Residual oil<br />

ÃÃÃÃÃÃÃÃ<br />

&NJTTJPOT PG 40 /0 /70$ $0 /) 541 1 BOE 1 <br />

In Table 3.22 the SO2, NOX, NMVOC, CO NH3, TSP, PM10 and PM2.5 emissions<br />

<strong>for</strong> road transport and other mobile sources are shown <strong>for</strong> 2010 in NFR<br />

sectors. For particulate matter (PM; TSP, PM10 and PM2.5), only the exhaust<br />

emission contributions are included in Table 3.22. Non-exhaust TSP, PM10<br />

and PM2.5 emissions are treated in a separate section below. The emission<br />

figures in the time series 1985-2010 are given in Annex 2.B.16 (NFR <strong>for</strong>mat)<br />

and are shown <strong>for</strong> 2010 in Annex 2.B.15 (CollectER <strong>for</strong>mat).<br />

From 1985 to 2010, the road transport emissions of SO2, NOX, NMVOC, CO<br />

and PM (all size fractions) have decreased by 99, 52, 84, 72 and 65 %, respectively<br />

(Figures 3.61-3.65), whereas the NH3 emissions have increased by 2232<br />

% during the same time period (Figure 3.66).<br />

For other mobile sources, the emission changes <strong>for</strong> SO2, NOX, NMVOC, CO<br />

and PM (all size fractions) are -88, -17, -28, -8 and -65 %, respectively (Figures<br />

3.68)-3.72). The NH3 emissions have increased by 17 % during the same<br />

time period (Figure 3.73).<br />

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