Fugitive Emissions from Fuels is a sub-sector in the Energy Sector. In the Danish emission inventory system fugitive emissions are treated in separate models. Fugitive Emissions from Fuels include emissions from five main groups of sources;

• “Fugitive emissions from solid fuels” includes emissions from storage of coal in coal piles. This source is only relevant for the Danish emission inventories in the case of emissions of particulate matter (PM). Other emissions related to mining are not occurring, as these emissions should be included in the inventory for the nation housing the coalmines.
• “Fugitive emissions from oil” includes emissions from extraction of oil and gas in the North Sea, loading of ships offshore and onshore and storage of oil at the Danish oil terminal. Further, it includes fugitive emissions from gasoline due to loading of tanker trucks and refuelling of cars at service stations.
  The relevant pollutants for emissions from oil are NMVOC and CH₄.
• “Fugitive emissions from refining” include emissions from the Danish refineries.
  This part of the inventory includes the pollutants NMVOC, CH₄ and SO₂.
• “Fugitive emissions from natural gas” includes emissions from transmission, storage, treatment and distribution of natural gas. Further, distribution of town gas is included.
  Emissions from natural gas include the pollutants NMVOC and CH₄.
• “Fugitive emissions from venting and flaring” includes both flaring offshore in the extraction industry, flaring in gas storage and treatment plants and in the refineries. Venting of gas occurs in gas storage plants. In Denmark venting of gas in offshore extraction is assumed to be negligible as controlled venting enters the gas flare system.
  The most important pollutants due to flaring are SO₂, NO_x, NMVOC, CH₄, CO and CO₂ but emissions of a number of other pollutants are included too; N₂O, particulate matter (PM), dioxin, heavy metals (HM) and polycyclic aromatic hydrocarbons (PAHs).

The most important pollutants in the fugitive sector are NMVOC, SO₂ and CH₄. The fugitive sector makes up 12 % of the national emission of NMVOC. The corresponding percentage of SO₂ and CH₄ are 6 % and 2 %, respectively.

Fugitive emissions from oil account for 53 % of the sectoral NMVOC emission and 57 % of the sectoral CH₄ emission. Hereof land based activities (onshore loading of ships and emissions from the oil terminal) account for 65 % and 44 %, respectively. Fugitive emissions from refineries account for 36 % of the NMVOC emission and 38 % of the CH₄ emission. There are two sources of fugitive SO₂ –refineries (45 %) and flaring (55 %).

Figure 1   Distribution of the fugitive emission of NMVOC and CH₄ for 2009.

Since 1990 the fugitive emissions of NMVOC has broadly followed the produced amount of oil and to a lesser degree of gas on the North Sea. Note that offshore loading is introduced in 1999 which generates a major increase of the total emission of NMVOC. The emission from offshore loading vary from year to year and is the dominating source for the NMVOC emission trend. Five major platforms were completed in the late nineties which is the main reason for the increased oil production and thereby the increase in the fugitive emissions from oil. The decrease in the NMVOC emission from service stations owe to introduction of new vapour control technologies both related to transfer of gasoline from tanker truck to storage tanks at the service stations (stage IB) and from storage tanks to car’s fuel tanks (stage II). There is only emission of NMVOC from service stations as gasoline does not evaporate CH₄.

The sectoral emission of CH₄ has been increasing from 1990 to 2009 again due to the increase of the amount of oil and gas production on the North Sea, which again is reflected in the emissions from extraction and from the oil terminal. The emission of CH₄ from loading of ships is minor as only around 5 % of the VOC emission is emitted as CH₄.

Figure 2   Time-series for fugitive emissions of NMVOC and CH₄ for the years 1990-2009.

The fugitive emission inventory is based on data for the oil/gas industry given in environmental reports, annual reports and on additional information gathered from the companies. Further, activity data, emissions and calorific values from the EU Emission Trading Scheme (EU ETS) are used. Other data sources are the Energy statistics and annual reports on the Danish Oil and Gas Production from the Danish Energy Agency and gas quality data from Energinet.dk.

In cases where data on emissions are not available, the emissions (E) are calculated as activity data (AD) multiplied by the corresponding emission factor (EMF). The emission factors are based on international literature or default values given in international inventory guidelines (EMEP/EEA Emission Inventory Guidebook). Emissions from extraction of oil and gas are, as the only fugitive source, calculated according to a default equation from the guidebook. Input data are production amounts for oil and gas and the number of platforms. The calculated emission is validated according to emission figures from the oil/gas sector for years when data are available.

For a more detailed description of the data and methodology for the inventory of fugitive emissions see the report “Emission Inventory for Fugitive Emissions in Denmark”.