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Annual Danish informative inventory report to UNECE. Emission ...

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170<br />

( = )& ⋅ () (27)<br />

where E = emission, FC = fuel consumption and EF = emission fac<strong>to</strong>r.<br />

The calculated emissions for other mobile sources are shown in CollectER<br />

format in Annex 2.B.14 for the years 2009 and as time-series 1985-<br />

2009 in Annex 2.B.15 (NFR format).<br />

(QHUJ\ EDODQFH '($ VWDWLVWLFV DQG 1(5, HVWLPDWHV<br />

Following convention rules, the DEA statistical fuel sales figures are<br />

behind the full <strong>Danish</strong> <strong>inven<strong>to</strong>ry</strong>. However, in some cases for mobile<br />

sources the DEA statistical sec<strong>to</strong>rs do not fully match the <strong>inven<strong>to</strong>ry</strong> sec<strong>to</strong>rs.<br />

This is the case for non road machinery, where relevant DEA statistical<br />

sec<strong>to</strong>rs also include fuel consumed by stationary sources.<br />

In other situations, fuel consumption figures estimated by NERI from<br />

specific bot<strong>to</strong>m-up calculations are regarded as more reliable than DEA<br />

<strong>report</strong>ed sales. This is the case for national sea transport.<br />

In the following the transferral of fuel consumption data from DEA statistics<br />

in<strong>to</strong> <strong>inven<strong>to</strong>ry</strong> relevant categories is explained for national sea<br />

transport and fisheries, non road machinery and recreational craft, and<br />

road transport. A full list of all fuel consumption data, DEA figures as<br />

well as intermediate fuel consumption data, and final <strong>inven<strong>to</strong>ry</strong> input<br />

figures is shown in Annex 2.B.13.<br />

1DWLRQDO VHD WUDQVSRUW DQG ILVKHULHV<br />

For national sea transport in Denmark, the fuel consumption estimates<br />

obtained by NERI (see 1.1.3 Activity data – national sea transport) are<br />

regarded as much more accurate than the DEA fuel sales data, since the<br />

large fluctuations in <strong>report</strong>ed fuel sales cannot be explained by the actual<br />

development in the traffic between different national ports. As a<br />

consequence, the new bot<strong>to</strong>m-up estimates replace the previous fuel<br />

based figures for national sea transport.<br />

There are different potential reasons for the differences between estimated<br />

fuel consumption and <strong>report</strong>ed sales for national sea transport in<br />

Denmark. According <strong>to</strong> the DEA, the latter fuel differences are most<br />

likely explained by inaccurate costumer specifications made by the oil<br />

suppliers. This inaccuracy can be caused by a sec<strong>to</strong>r misallocation in the<br />

sales statistics between national sea transport and fisheries for gas oil,<br />

and between national sea transport and industry for heavy fuel oil (Peter<br />

Dal, DEA, personal communication, 2007). Further, fuel sold for vessels<br />

sailing between Denmark and Greenland/Faroe Islands are <strong>report</strong>ed<br />

as international in the DEA statistics, and this fuel categorisation<br />

is different from the IPCC guideline definitions (see following paragraph<br />

“Bunkers”).<br />

Following this, for fisheries and industry the updated fuel consumption<br />

time-series for national sea transport lead, in turn, <strong>to</strong> changes in the fuel<br />

activity data for fisheries (gas oil), industry (heavy fuel oil) and international<br />

sea transport, so the national energy balance can remain unchanged.<br />

For fisheries, fuel investigations made prior <strong>to</strong> the initiation of the work<br />

made by Winther (2008a) have actually pointed out a certain area of in-

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